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Species richness of gall midges (Diptera, Cecidomyiidae) in Europe (West Palaearctic): biogeography and coevolution with host plants

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Acta Soc. Zool. Bohem. 73: 87–156, 2009
ISSN 1211-376X
Species richness of gall midges (Diptera: Cecidomyiidae) in Europe (West
Palaearctic): biogeography and coevolution with host plants
Marcela SKUHRA & Václav SKUHRA
Bítovská 1227, CZ–140 00 Praha 4, Czech Republic; skuhrava@quick.cz
Received 25 September 2009; accepted 21 December 2009
Published 2 December 2010
Abstract. The present fauna of the family Cecidomyiidae Macquart, 1838 in Europe includes 1800 valid species in 270
genera. It is divided into three subfamilies: Lestremiinae Rondani, 1840 with 280 species in 33 genera, Porricondylinae
Enderlein, 1936 with 310 species in 62 genera and Cecidomyiinae Rondani, 1840 with 1210 species in 175 genera.
Only the last subfamily includes gall-causing and plant-inhabiting species. For the family Cecidomyiidae, Europe
is the most species-rich continent of the world. On average, each gall midge genus contains 6,6 species. The most
species-rich genus is Dasineura Rondani, 1840, with 230 species, followed by Contarinia Rondani, 1860, with 135
species. On the basis of the larval feeding habits, the family Cecidomyiidae may be divided into three biological
groups: 51% of species are phytophagous, 39% mycophagous, 8% zoophagous and the biology of about 2% remains
unknown. All species of the subfamilies Lestremiinae and Porricondylinae are mycophagous.
Fundamental sources for evaluation of the family Cecidomyiidae in Europe are 40,000 records about their
occurrence and distribution gathered by the present authors at more than 1850 localities in 17 countries of mainland
Europe and nine islands in the Mediterranean at altitudes from sea level up to 2645 m a. s. l. in the Alps in the period
1955–2009. All samples were obtained using the time and area unit collection method and results were enriched
by data collected by earlier researchers. Evaluation was based on identified and valid species, not on unidentified
and unnamed gall-inducing organisms.
This abundant data enabled production of maps of occurrence of individual gall midge species of the Czech
Republic, Slovakia, France, Spain, Portugal, Poland and Austria, and also graphs showing the vertical occurrences
of some species in several countries of Europe. These were published in several summarizing articles (Skuhravá
1991, 1994a, b, Skuhravá & Skuhravý 2009a, Skuhravá et al. 2005, 2006). The accumulated data makes it possible
to determine zoogeographical characteristics of single species occurring in Europe.
Here we summarize information about the occurrence of gall midge species of the main genera in Europe and
present results in maps of the following genera: Dasineura Rondani, 1840, Contarinia Rondani, 1860, Asphondylia
Loew, 1850, Rhopalomyia Rübsaamen, 1892, Lasioptera Meigen, 1818, Stefaniola Kieffer, 1913, Rabdophaga
Westwood, 1847, Jaapiella Rübsaamen, 1915, Resseliella Seitner, 1906, Macrolabis Kieffer, 1892, Baldratia
Kieffer, 1897, and Mayetiola Kieffer, 1896.
Evaluation of species richness using the average species number per locality showed that Hungary, with
29 species, France with 28 species and the Czech Republic with 26 species are the countries with the highest gall
midge species richness in Europe. The average species number decreases to the north and to the south of Europe.
Evaluation of species richness using the species density calculated for country or island unit area of 1000 km2
makes it possible to divide countries into five density groups. TheCzech Republic and South Tyrol (northern Italy)
are the countries with the highest species density, each with 189 gall midge species occurring per 1000 km2. Gall
midges of Europe belong to the following zoogeographic or biogeographic units: 71% are European species, 12%
Eurosiberian, 9.5% Mediterranean including Submediterranean, 1.3% Palaearctic or Euroasian, 4.5% Holarctic,
0.4% cosmopolitan and 1.3% are alien species.
Gall midge species are not uniformly distributed in Europe. Many species were found only once at the type
locality, some species are rare, others occur moderately frequently and only a few species occur very frequently.
It is possible to divide all species found in the area under study into six frequency groups by using the first six
members of the geometrical progression with quotient “2” and coefficient “a”, as follows: a.20 + a.21 + a.22 + a.23
+ a.24 + a.25. The most frequent species in the whole of Europe is Jaapiella veronicae (Vallot, 1827) causing galls
on Veronica chamaedrys; in northern Europe it is Iteomyia capreae (Winnertz, 1853) on Salix caprea; in southern
Europe both Phyllodiplosis cocciferae (Tavares, 1901) and Dryomyia lichtensteinii (Löw, 1878) causing galls on
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Quercus coccifera, Q. ilex and Q. suber are equally frequent. Each part of Europe has its own gall midge species
which is the most frequent in the area characterized by particular conditions of the environment. Species number
changes with geographic position. The highest species number occurs in the temperate part of Europe covered
with mixed forests between latitudes 45° and 52° North. Species number decreases to the north and to the south
and is influenced importantly by climatic factors. Central Europe has favourable weather with mild temperatures
and with a relatively sufficient amount of rainfall. Species number changes with increasing altitude of localities
together with changes in composition of vegetation: in lower parts the gall midge species number is relatively high
and it decreases with increasing altitude. Rhopalomyia luetkemuelleri (Thomas, 1893) causing galls on Artemisia
spicata and Jaapiella alpina (Löw, 1885) inducing galls on Silene acaulis are two gall midge species found at the
highest altitudes in Europe – at elevations of 2500–2700 m a. s. l. in the Alpine and subnivale zones. Oligotrophus
juniperinus (Linnaeus, 1758) inducing galls on Juniperus communis, occurs over a large altitudinal span including
sites in the planare zone at 190 m a. s. l. up to 2348 m a. s. l. in the Alps. It has considerable ecological tolerance
and has been recorded over a vertical range of more than 2000 m. Gall-inducing gall midges of Europe are one of
the best known gall-causing groups of animals in the world. They have to be the most suitable group for prognosis
of gall midge species numbers and their galls in the future. On the basis of data on the occurrence and distribution
of gall midge species gathered from the times of Linnaeus to the present it may be predicted that in Europe the
number of valid species in the family Cecidomyiidae may be increased by about four hundred to 2200 valid species
and the number of galls caused by gall midges by about two hundred to 1400 sorts of galls by the year 2050.
In Europe 915 gall-causing and plant-inhabiting species of the subfamily Cecidomyiinae are associated with 280
genera of host plants that belong in 72 plant families. On average one plant genus hosts 3,26 species of gall midges.
Only two gall midge species are associated with the Pteridophyta, 27 species with the Gymnospermae, 886 species
with the Angiospermae, of which 109 species are on Monocotyledones, and 777 species on Dicotyledones. Gall
midges are more closely associated with some plant families in which they find more favourable host plant species
and genera for their development. The family Fabaceae hosts the highest number of gall midge species – 123 species
– and the family Asteraceae hosts 104 gall midge species. In Europe about 70% of gall-inducing species and plant
inhabiting species of the subfamily Cecidomyiinae are associated with herbaceous plants and only 30% with trees
and shrubs. For the comparison of relationships between gall midges and host plants we introduce the formula
– the index of mutual gall midge species and plant species occurrence:
IGS-PSO= NPS/NGMS where NPS is the number of plant species in a particular country and NGMS is the
number of gall midge species occurring in the country. This index indicates the degree of mutual occurrence of
gall midges on host plants in particular parts of Europe. The analysis of relationships between gall midges and host
plants produced the surprising finding that although the species number of flowering plants in Europe increases
towards the south, the species number of gall midges decreases.
Galls of gall midge species are not equally distributed on the organs of their host plants. Species of the genus
Dasineura Rondani, 1840 cause galls mainly on buds and leaves; of the genus Contarinia Rondani, 1860 on
flowers; of Asphondylia Loew, 1850 on flowers and fruits, of Rabdophaga Westwood, 1847 on stems and buds;
of Rhopalomyia Rübsaamen, 1892 on buds; of Jaapiella Rübsaamen, 1915 on buds and flowers, species of the
genus Macrolabis Kieffer, 1892 are mainly inquilines in galls of other gall midges and the species of Mayetiola
Kieffer, 1896, Lasioptera Meigen, 1818, Planetella Westwood, 1840 and Resseliella Seitner, 1906 develop in
galls mainly on stems. In Europe 94 gall midge species are associated with twelve main broad-leaved tree species
and 23 gall midge species with six coniferous tree species. Quercus robur is the host tree species with the highest
species gall midge number (15 species), followed by Populus tremula and Quercus cerris (each with 13 species),
Betula pendula and Tilia platyphyllos (each with 10 species).
Coevolution of gall-inducing and plant inhabiting species of the family Cecidomyiidae developed in parallel
with two groups of vascular plants, the Pteridophyta and the Spermatophyta, a long time ago in the geological
history of the Earth. One fossil record of Sequoiomyia kraeuseli (Möhn, 1960) found in fossil cones of Sequoia
langsdorfii (Taxodiaceae) supports the early coevolution of gall midges with conifers. Fossil galls of ten gall midge
species provide evidence of the coevolution of gall midges with flowering plants in the Miocene and Pliocene
of the Tertiary in various parts of Europe. The gall-inducing and plant inhabiting gall midges of the subfamily
Cecidomyiinae probably started to develop at the end of the Mesozoic when they entered into interactions with
developing groups of flowering plants. The main development of gall-inducing and plant inhabiting gall midges
came in the Pliocene and Miocene of the Tertiary.
This article is illustrated with 40 figures, including maps of geographical distribution of the main genera of
the subfamily Cecidomyiinae, maps of distribution areas of several interesting gall midge species and graphs
illustrating summaries of results obtained during investigations in Europe.
Distribution, Diptera, Cecidomyiidae, Lestremiinae, Porricondylinae, Cecidomyiinae, Palaearctic, West
Palaearctic, Europe, species number, species richness, frequency, geographic gradients, biogeography,
zoogeography, plant-animal relations, coevolution with host plants.
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CONTENTS
Abstract .......................................................................................................................................... 87
Introduction ......................................................................................................................................... 89
Material and methods ........................................................................................................................................................ 92
Results ............................................................................................................................................................................... 95
Fauna ........................................................................................................................................................................... 95
Species richness .............................................................................................................................................. 97
Species density .......................................................................................................................................................... 103
Species richness of the main genera .......................................................................................................................... 106
Geographic distribution ............................................................................................................................................. 113
Geographic position and geographic gradients ......................................................................................................... 123
Climatic factors ......................................................................................................................................................... 125
Vertical distribution ................................................................................................................................................... 126
Frequency .................................................................................................................................................................. 130
Possibilities of findingadditional gall midge species number in Europe .................................................................. 132
Gall midges and host plants ....................................................................................................................................... 134
Mutual occurrence of gall midges and host plants .................................................................................................... 142
Distribution of galls on host plants ............................................................................................................................ 144
Abundance of gall midge species on host plant species ............................................................................................ 144
Coevolution of the family Cecidomyiidae with plants ............................................................................................. 145
Factors affecting gall midge species richness ........................................................................................................... 148
Acknowledgements ......................................................................................................................................................... 150
References ....................................................................................................................................................................... 150
INTRODUCTION
The Cecidomyiidae is one of the most species-rich families of Diptera and also contains the
largest group of gall-inducing animals in the world. Gagné (2004), in his World Catalog, listed
5451 species in 598 genera of living and fossil gall midges. Altogether 3113 species in 344 genera
occur in the Palaearctic Region of which more than 1800 species in 270 genera occur in Europe
(Skuhravá 2006a). The family Cecidomyiidae Macquart, 1838 is currently classified under three
subfamilies: Lestremiinae Rondani, 1840, Porricondylinae Enderlein, 1936 and Cecidomyiinae
Rondani, 1840. Only larvae of Cecidomyiinae are able to induce galls on host plants, larvae of
three subfamilies are mycophagous or mycosaprophagous. Adults are usually very small, incon-
spicuous flies but the galls (in Latin: cecidium) that are caused by their larvae on various organs
of host plants are strange and striking formation (hence the common name “gall midges”). Larvae
of some species live free in flower heads or stems of plants without making galls and others are
mycophagous or saprophagous. Zoophagous larvae are predators of larvae of other gall midges,
of aphids, mites, coccids, or other small arthropods and some of them may be used in biological
control of pests. Larvae of some species live as inquilines in galls of other gall midges or other
insects. The biology of many species of gall midges caught as adults in nature is completely unk-
nown (Skuhravá 1986, 1997a, Skuhravá et al. 1984a, b). In Europe about sixty gall midge species
are economically important, of them forty species cause damage to agricultural plants (Darvas et
al. 2000) and twenty to forest trees (Skuhravá & Roques 2000).
The Palaearctic Region is the largest zoogeographic or biogeographic region of the world oc-
cupying an area of about 52 millions km2 (about 39% of the Earth surface). It includes arctic and
temperate Eurasia and all islands surrounding the continent in the Arctic, in the sea of Japan and
the eastern half of the North Atlantic, the Mediterranean North Africa and the northern and central
parts of the Arabian Peninsula. In Asia the customary boundary has the High Himalayas chain as
main divider and the boundary in China and Japan runs at Northern Latitude 30° (Udvardy 1975,
Soós & Papp 1986). The Palaearctic Region is usually divided into two parts, namely the West
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Palaearctic, and the East Palaearctic (sensu lato), that includes an extensive area from the Ural
Mountains across Siberia to the Kamchatka Peninsula in the most eastern part of Russia, or into
four subregions, viz. Euro-Siberian, Mediterranean, Central-Asian, and East-Palaearctic (sensu
stricto), situated in eastern Asia and including Japan and its islands, the Korean Peninsula, part
of Russia and part of China.
The West Palaearctic consists of the western part of the Euro-Siberian subregion (i.e. Europe)
and of the Mediterranean subregion, together including 48 countries and several islands that differ
substantially from each other by the geographic position and mainly by various areas. It is very
difficult to compare gall midge species numbers of these countries and to evaluate them. For
example, France is the largest European country, occupying an area of 551,255 km2 and the gall
midge fauna includes 668 species of which 581 belong to Cecidomyiinae including gall-inducing
species (Skuhravá et al. 2005). On the other hand, Liechtenstein situated between Austria and
Switzerland is the smallest country occupying an area of 157 km2 and its gall midge fauna inclu-
des 65 species (Skuhravá & Skuhravý 1993a). It was therefore necessary to find a method that
would make it possible to compare these values. We used two methods for evaluation of species
numbers of individual country: species number per unit area and average species number per
locality of area under study.
Europe is one of the five continents of the Earth covering an area of about 10,180,000 km2. It
is bounded to the north by the Arctic Ocean, to the west by the Atlantic Ocean, to the south by
the Mediterranean Sea, to the southeast by the Caucasus Mountains and the Black Sea and the
waterways connecting the Black Sea to the Mediterranean. To the east, Europe is divided from
Asia by the water divide of the Ural Mountains, the Ural River, and by the Caspian Sea. For the
project Fauna Europaea, the external geographic boundaries are defined as follows: the defined
area consists of the European mainland and Mediterranean islands, plus the Macaronesian islands
(Azores, Canary Islands, Madeira; excluding Cape Verde Islands), Franz Josef Land and Novaya
Zemlya, with Western Kazakhstan excluded (Fig. 1).
In Europe the main natural vegetation is forest. In temperate Europe, mixed forests with both
broadleaved and coniferous trees dominate. The most important species in central and western
Europe are broadleaved trees of Fagus sylvatica, Quercus robur and Q. petraea. In the north,
the taiga is a mixed forest with dominant trees of Picea abies, Pinus sylvestris and Betula spp.;
further north within Russia and extreme northern Scandinavia, the taiga changes to tundra. In the
Mediterranean the dominant tree is Olea europaea which is very well adapted to its arid climate.
In the semi-arid Mediterranean region scrub forests occur. a narrow east-west oriented strip of
Eurasian grassland, the steppe, extends eastwards from Ukraine and southern Russia as far as Hun-
gary. In Europe animals and plants have been substantially affected by the presence and activities
of man since ancient times. With the exception of Scandinavia and northern Russia, few areas of
untouched wilderness and original nature are at present found here, except for various national
parks. In the past, most (about 90%) of Europe was covered by forests. They extended from the
Mediterranean to the Arctic Ocean in the north. About half of these original forests disappeared
through the centuries owing to deforestration.
Southern parts of Europe, forming a zoogeographic sub-unit called the Mediterranean subre-
gion partly borders the Mediterranean Sea and also includes the northern part of Africa and part
of western Asia. The climate of this part is mild, winters are rainy and summers are hot and dry.
The landscape is covered with forests, woodlands and scrub. This part is one of the world‘s most
endangered biogeographic regions. Only about 4% of the original vegetation remains. Man and
his activities, including overgrazing, deforestation and conversion of lands for pasture, agriculture,
or urbanization, have degraded much of the region. Formerly this region was mostly covered with
forests and woodlands, but heavy human use has reduced much of the region to the sclerophyll
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shrublands known as chaparral, matorral, maquis and garrigue. At present, 48 countries of vari-
ous size comprise Europe. Of them, the European part of Russia is the largest both in area and
population. The level of knowledge about galls on plants and gall-inducing organisms is very
uneven in Europe. Some countries have a long tradition and many researchers contributed to the
knowledge which resulted in high species numbers of the family Cecidomyiidae being recorded
in Germany, France, United Kingdom, Czech Republic, Poland and Austria. Up to the end of
the twentieth century only a few records of gall midge species and their galls were known from
Greece and islands in the Mediterranean Sea. At present we have little information about gall
midges and their galls in Albania and Moldova.
Gall midges are the richest group of gall-inducing animals in Europe. Houard (1908–1909) in
his two-volume book on plant galls of Europe and the Mediterranean included 6239 sorts of galls
that are induced by 1450 species of animals belonging to various taxonomical groups. Gall midges
(Diptera: Cecidomyiidae) totalled 420 species are the richest group of all gall-inducing animals,
constituting 29%. Buhr (1964–1965), in identification keys for galls on the plants of Central and
Northern Europe, recorded gall midges as the richest group, including 580 species, i.e. 36% of
all insect species inducing galls. Kolomoets et al. (1989) recorded 328 gall-inducing species of
Diptera associated with plants in the European part of the USSR. Of those, 301 species (92%)
belong to Cecidomyiidae and 25 species to six other dipteran families. In Japan, situated in the
Eastern Palaearctic, the gall midges with 628 species (44%), including described and undescribed
species, are the richest group of gall-inducing arthropods (Yukawa & Masuda 1996). Of those,
only 176 species are described species.
Fig. 1. Europe and its boundary (black line) as defined in the Fauna Europaea (2007) and its main geographical features
shown in different colours: lowlands from sea level to 200 m a. s. l. (green); hilly country from 200 to 500 m a. s. l. (yel-
low); uplands from 500 to 900 m a. s. l. (pale brown); lower mountains from 900 to 1800 m a. s. l. (brown); upper moun-
tains from 1800 to 2400 m a. s. l. and over (dark brown). Important islands: 1 – Iceland; 2 – Faroe Islands; 3 – Azores;
4 – Madeira; 5 – Canary Islands; 6 – Cyprus.
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We summarized knowledge about gall midges in several European countries from various
points of view, including a review of the history of research, evaluation of contributions of earlier
researchers to the progress of studies, the biology, zoogeography, relations of gall midges to host
plants and economic importance of gall midges. We published such summarizing articles about
gall midges of Slovakia (Skuhravá 1991), of the Czech Republic (Skuhravá 1994a, b), of Greece
(Skuhravá & Skuhravý 1997), of France (Skuhravá et al. 2005), of Denmark (Skuhravá et al.
2006), of the Iberian Peninsula (Skuhravá et al. 2006), of Poland (Skuhravá et al. 2008) and of
Austria (Skuhravá & Skuhravý 2009a).
The aim of our present article is to show the species richness of gall midges in Europe and the
West Palaearctic, the abundance, density and frequency of gall midges and factors influencing
them, including geographic distribution and the effect of geographic gradients for distribution of
species numbers, the influence of climatic factors on species distribution and to predict increa-
sing of species number in the future. We analyse relations of gall midges to host plants and their
botanical families, try to elucide causes of their diversity and to indicate the probable process of
coevolution of the family Cecidomyiidae with plants in the history of the Earth.
MATERIAL AND METHODS
During the period 1955–2009 we investigated gall midges in 17 countries and nine islands at more than 1850 localities
spread throughout Europe from the northernmost situated locality at Harstad in the island Hinnoya in northern Norway
to the southernmost situated locality in Malta in the Mediterranean. Localities for our investigations were selected from
the sea level – some at the seaside of the Atlantic Ocean and many along the coast of the Mediterranean, and at various
altitudinal zones starting with lowlands up to mountains with the highest situated locality at an altitude of 2645 m a. s. l.
at Col du Galibier in Hautes Alpes in France. We gathered about 40,000 records about the occurrence of gall midge spe-
cies in Europe and in nine islands in the Mediterranean. These records are a unique collection of such data dealing with
a group of gall-inducing arthopods and they make it possible to evaluate the Cecidomyiidae from several points of view
and to determine factors that influence their species richness in Europe. Important is the fact that our considerations on
species richness and evaluations of factors influencing them are based on valid species, e.i. on identified species, not on
unidentified and unnamed gall-inducing organisms (Fig. 2).
During our faunistic investigations in various countries of Europe and in Asia we used at each locality the time and
area unit collection method that we established in 1955. This involves surveying each selected locality visually by walking
through it slowly over a period of at least one up to three hours. Two persons walk through various biotopes at the locality
and search for gall midges galls and collect them on herbs, shrubs and trees and examine visually buds, leaves, flowers,
fruits and stems of herbaceous plants, shrubs and trees. The altitude and short characteristics of biotopes are noted. All
findings are recorded, including notes about the local abundance of species. Each locality was investigated only once by
this method. During excursions, several specimens of each host plant with galls were put in separate small plastic bags.
All species that were found were recorded in the protocol and all collected material was prepared. Several specimens of
each host plant with galls were preserved as herbarium items, several plants with galls were kept in plastic bags to obtain
living larvae, several plants with galls were placed in small emergence cages to obtain adults and finally several galls
with larvae were put into vials with 75% alcohol for future morphological studies or for studies of the digestive system
of larvae. Such samples taken from various habitats or microhabitats are very important.
The localities where we investigated gall midges in the Czech Republic, Slovakia and Austria are given in Fig. 3.
Localities were selected throughout the whole territory using the map with Ehrendorfer’s network (Ehrendorfer 1973), as
far as possible examining one locality in each oblong of a size 11×12 km. In a similar way we prepared our investigations
in Italy, Switzerland, Greece and other countries.
All data obtained during our investigations of gall midge faunas in Europe, was augmented with data of earlier authors,
and evaluated and analysed from two points of view, viz. from the geographic and from the zoological points of view
using the methods of Skuhravá (1987, 1994a, b, 1997b). From the geographic point of view, the horizontal occurrence is
presented by various species numbers (absolute species numbers found) and by average species numbers in countries of
Europe and by numbers of species related to area unit of 1000 km2. The vertical occurrence is shown as average species
numbers in the rising altitudinal zones. From the zoological point of view, it is possible to elaborate the characterization
of a particular species (zoogeographic diagnosis) and elaborate maps of distribution areas of a particular species which
may be compared with distribution areas of pertinent host plant species.
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Fig. 2. Distribution of sites in Western Europe where the investigations of the family Cecidomyiidae were carried out in
countries and islands by the present authors (black circles) in the period 1955–2009, or where summaries of information
were published by other authors (white circles). See Table 1 for the abbreviations for countries; numbers for islands:
1 – Faroe Islands, 2 – Mallorca, 3 – Corsica, 4 – Sardinia, 5 – Sicily, 6 – Malta, 7 – Corfu, 8 – Samos, 9 – Crete.
We gathered not only our own data on occurrence of gall midges in European countries that we obtained in the course
of our expeditions but we collected also data on occurrence of gall midge species in countries of Europe found by earlier
researchers from the middle of the nineteenth century, when various researchers started investigations of galls, up to
the present. These data about occurrence were included in the part devoted to distribution of each gall midge species in
the Catalogue of Palaearctic Diptera (Skuhravá 1986). The paucity of records of gall midge species in some countries
motivated us to investigate in countries where the species number was low, as for example in Norway, Greece, northern
Italy (South Tyrol) and the islands in the Mediterranean.
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Fig. 3. A–C. Distribution of localities in Central Europe where planned systematic faunistic investigations of the family
Cecidomyiidae were carried out by the present authors: a – in the Czech Republic investigations were made at 670
localities at altitudes from 116 m a. s. l. to 1603 m a. s. l. at Mount Sněžka, in the Giant Mountains, the highest point of
the country, in 1957–1982 (Skuhravá 1994a, b); b – in Slovakia investigations were made at 336 localities at altitudes
from 110 m a. s. l. to 2000 m a. s. l. in the High Tatras in 1969–1976 (Skuhravá 1991); c – in Austria investigations were
made at 274 localities situated at altitudes from 115 m a. s. l. up to 2500 m a. s. l. in the Alps in 1967 and 1991–1993
(Skuhravá & Skuhravý 2009a).
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In Table 1, we summarized fundamental data and source of information on the Cecidomyiidae in alphabetical order of
countries and islands of Europe, abbreviations of countries as used in the maps; total gall midge species of Cecidomyiidae,
followed totals for the three subfamilies, the Lestremiinae, Porricondylinae and Cecidomyiinae; number of localities
examined by the present authors and the references. Islands belonging to Europe are here considered to be independent
geographic units, although some of them are components of continental countries as indicated in parentheses; for Spain
and Portugal, see the chapter “Area of study” in the catalog of Carles-Tolrá Hjorth-Andersen (2002). Cyprus and Malta are
independent island countries. The present level of knowledge in countries of Europe and in islands in the Mediterranean,
given as species numbers of Cecidomyiidae, is shown in Fig. 4.
It is necessary to emphasize that we comprehend and interpret the family Cecidomyiidae as a whole mainly in the
introductory parts of our article. In the parts devoted to evaluation of results we deal mainly with part of it – the subfamily
Cecidomyiinae – that includes gall-inducing and plant-inhabiting species which are associated with host plants. Members
of the subfamilies Lestremiinae and Porricondylinae are mycophagous and are not associated directly with host plants.
RESULTS
Fauna
The fauna includes all the species of animals found in a particular region, period, or special en-
vironment. The following six faunal regions or realms are recognized on the basis of terrestrial
animal species. The fauna of the Diptera is known from each of these regions and relevant cata-
logues have been published. We give in the following part the authors that prepared the family
Cecidomyiidae for catalogues of various parts of the world.
The fauna of Cecidomyiidae of the Palaearctic region including Eurasia, i.e.Europe and Asia
north of the tropics, and northern Africa, was prepared by Skuhravá (1986); the fauna of the Nearctic
region consisting of North America except for tropical Mexico by Foote (1965) and Gagné (1989a);
of the Neotropical region (situated in South and Central America including tropical Mexico) by
Gagné (1968, 1994); of the Afrotropical or Ethiopian region of Africa south of the Sahara and
part of southern Arabia by Harris (1980); of the Indomalayan or Oriental region covering tropical
Asia and associated continental islands by Gagné (1973) and Grover (1981); of the Austral-Asian
and Oceanian regions including Australia, New Guinea and islands in Oceania by Gagné (1989b).
In addition, Nearctic and Palaeartic (including Eurasia and northern Africa) regions are usually
combined into the Holarctic region. Many changes have occurred in the composition of faunas
of all regions in the last twenty years. They are reflected in the world catalog of Gagné (2004)
and in the analysis of world faunas in the article by Skuhravá (2006a).
The present or contemporary or extant fauna of the family Cecidomyiidae known in Europe
totals 1800 species in 270 genera (Table 2). Europe, a small continent if it is classified by size, is
the most species-rich continent of the world in terms of known species of gall midges. On average
each gall midge genus includes 6,6 species. Most genera are monotypic, containing only a single
species. On the other hand there are several large genera with many species, as follows: the species
richest genus Dasineura (230 species), followed by Contarinia (135 species), Asphondylia (50
species) and Rabdophaga (40 species) (see Table 7). The distribution of gall midge species in
Europe where they form single small faunas of countries and islands is given in Fig. 4.
The gall midges occurring in Europe may be divided into three main biological groups on the
basis of the larval feeding habits. If we evaluate the family Cecidomyiidae as the whole, we obtain
the following data: 51% of species are phytophagous, larvae of which feed on or in plant tissue,
forming galls or inhabiting plant organs without making galls; 39% are mycophagous, larvae of
which are associated with various fungi; in this group are usually included xylophagous species;
8% are zoophagous, larvae of which feed as predators on small animals, especially insects, and
the biology of about 2% remains unknown. See Table 2 and Figs 5, 6. If we evaluate the subfa-
mily Cecidomyiinae as separate unit that contains 1210 species, the separation of species into
96
Table 1. Sources of information on the family Cecidomyiidae in Europe. Abbreviations: CA – country abbreviation;
T – total species number; L – Lestremiinae; P – Porricondylinae; C – Cecidomyiinae; n – number of localities
country CA T L P C n references
Andorra AND 30 2 28 Skuhravá et al. 1996, 2002, 2006
Albania AL 19 19 Skuhravá 1986 (including 8 alien species)
Austria A 396 31 13 352 274 Skuhravá & Skuhravý 1967, 1992c, 1995, 2009a,
Skuhravá & Franz 1989
Belarus BY 38 0 0 38 Fiedorowiczówna 1931, Perepeczko-Baumanowa
1935
Belgium B 140 5 5 130 Lambinon 1957, 1958, 1976, Gosseries 1991
Bosnia and BH 169 169 Simova-Tošič et al. 2007
Herzegovina
Bulgaria BG 240 240 46 Skuhravá et al.1991
Canary Is. (Spain) 3 3 Skuhravá et al. 2002
Corfu (Greece) 49 49 8 Skuhravá & Skuhravý 2006b
Corsica (France) 60 60 10 Skuhravá & Skuhravý (in prep.)
Crete (Greece) 38 38 10 Skuhravá & Skuhravý 1997a
Croatia CR 232 232 Simova-Tošič et al. 2004
Cyprus CY 32 32 17 Skuhravá & Skuhravý 2004a
Czech Republic CZ 590 13 13 564 670 Skuhravá 1994a, 1994b, 2006b, 2009
Denmark DK 307 18 14 275 22 Skuhravá et al. 2006
Estonia 93 48 45 0 Spungis 1998, Spungis & Jaschhof 2000
Faroe Is. (Denmark) 5 5 5 Skuhravá & Skuhravý 2009c
Finland FIN 135 4 27 104 Hackman 1980
France F 668 33 54 581 17 Skuhravá & Skuhravý 2004c, d, Skuhravá et al. 2005
Germany D 836 125 58 653 26 Meyer & Jaschhof 1999
Greece GR 167 56 Skuhravá & Skuhravý 1997a, 2009b
211 Skuhravá & Skuhravý (unpubl.)
Hungary H 332 332 22 Skuhravá & Skuhravý 1999
Ireland IRL 87 87 O’Connor et al. 1999
Italy I 324 7 2 315 Skuhravá & Skuhravý 1994, Skuhravá 1995
508 27 10 471 14 Skuhravá & Skuhravý (unpubl.)
Italy, South Tyrol 312 312 124 Skuhravá et al. 2001, 2002, Skuhravá & Skuhravý
2003, 2005a, b, 2006a, 2007b, 2009d
Latvia LV 506 113 129 264 Spungis 2002, 2003, Spungis & Jaschhof 2000
Liechtenstein FL 65 65 9 Skuhravá & Skuhravý 1993a
Lithuania LI 224 25 35 164 Pakalniškis et al. 2000, Spungis & Jaschhof 2000
Luxembourg L 75 75 Lambinon et al. 2001
Macedonia MK 148 148 Simova-Tošič et al. 2007
Madeira (Portugal) 18 18 Skuhravá 2008
Mallorca (Spain) 33 33 7 Skuhravá & Skuhravý 2004b
Malta M 36 36 17 Skuhravá et al. 2002
Moldova MD 5 5
Montenegro MNE 85 85 Simova-Tošič & Skuhravá 2001
Netherlands NL 340 20 15 305 Nijveldt & Beuk 2002
Norway N 170 48 4 112 15 Skuhravá & Skuhravý (in preparation)
Poland PL 320 17 397 Skuhravá & Skrzypczyńska 1983, Skuhravá et al.
463 49 2008
Portugal P 122 122 Skuhravá et al. 1996, 2002, 2006
Romania RO 315 2 9 304 23 Skuhravá et al. 1972
Russia (European) RU 650 122 128 400 Skuhravá, Skuhravý & Prziboro (in prep.)
Samos (Greece) 34 34 8 Skuhravá & Skuhravý 2006b
Sardinia (Italy) 44 44 15 Skuhravá & Skuhravý 2002
Serbia SE 283 283 Simova-Tošič et al. 2000, Skuhra& Skuhravý 1964
Sicily (Italy) 89 89 Skuhravá et al. 2007
Slovakia SK 362 2 5 355 336 Skuhravá 1991, 2006b, 2009
97
biological groups is quite different: phytophagous gall midges comprise 76%, zoophagous 12%,
mycophagous including xylophagous 9% and for 3% the larval biology remains unknown.
Species richness
The term species richness is used here for the records of all species occurring in Europe, com-
pared with species numbers of other parts of Palaearctic Region or with other continents. The
term species density is used for the number of species calculated for each country on a unit area
of 1000 km2 (i.e. 31.62×31.62 km).
A total of 1800 gall midge species (i.e. valid, described species) of the family Cecidomyiidae
are known from the whole territory of Europe (Table 2). Species are not equally distributed in
European countries. The occurrence of gall midge species in a country may be influenced by se-
veral factors, mainly by the geographic position, size of the country, composition of vegetation,
environmental changes and also by investigations that were done in a country by researchers in the
past and by investigations that are carried out at present. We tried to analyse some of these factors
on the basis of our rich experience obtained during long-term studies of this group in Europe.
In Table 3 we compare species numbers in countries of Europe ranked according to geogra-
phic area and simultaneously we evaluate the level of knowledge and level of recent reseach
of the family in each country. In the column called level of knowledge we evaluate results of
investigations of the family obtained by researchers in the past which are expressed in the pre-
sent species number of the family. For evaluation of the level of knowledge we use the adapted
classification scale given in the publication of Merz et al. (1998) where they evaluate the quality
of knowledge of dipteran families in Switzerland, viz. as very good, good, medium, poor or very
poor. The level of recent research in the last column of the table is evaluated for the period of
Table 1. (continued)
country CA T L P C n references
Slovenia SLO 219 219 Simova-Tošič et al. 1996, Skuhra& Skuhravý 1964
Spain E 229 17 0 212 Skuhravá et al. 1996, 2002, 2006, Skuhravý &
Skuhravá 1999
Sweden S 378 102 7 266 Skuhravá & Skuhravý (in prep.)
Switzerland CH 237 3 6 228 56 Skuhravá & Skuhravý 1997b, Merz et al. 1998
Turkey TR 70 70 Skuhravá et al. 2005
Ukraine UA 298 93 39 166 Skuhravá, Skuhravý & Berest (in prep.)
United Kingdom UK 620 62 32 526 7 Harris 1976, Chandler 1998, Skuhravá & Skuhra
2007b
Table 2. Number of species and genera of Cecidomyiidae in Europe (Skuhravá 2010, unpublished data) and separation of
gall midge species into biological groups. Abbreviations: n – number of, myco – mycophagous, phyto – phytophagous,
xylo – xylophagous, zoo – zoophagous, un – unknown biology
subfamily n genera n species myco xylo phyto zoo un
Lestremiinae 33 280 280 0 0 0 0
Porricondylinae 62 310 310 0 0 0 0
Cecidomyiinae 175 1210 75 35 915 150 35
total 270 1800 665 35 915 150 35
% 100 37 2 51 8 2
98
Fig. 4. Distribution of species of the family Cecidomyiidae in countries and islands of Europe in 2009; islands belonging
to Europe are here considered to be independent geographic units although some of them are components of continental
countries. Cyprus and Malta are independent island countries.
about the last twenty years (1989–2009). We use the following three categories: no, few or many
investigations (Table 3).
The species number does not depend directly on the size of the country. European part of
Russia has the largest area but from the point of view of its species richness (600 species) is in
third place. Ukraine is second in area but with about 300 species only in the sixteenth place from
the point of species richness. Two large countries, France and Germany, are among the first five
99
countries both from the point of view of area and species numbers. Finland with a large area of
337,030 km2 has only 135 species, in contrast to Bulgaria occupying a much smaller area (about
one third the area of Finland) where 240 species are known to occur. On the other hand, from
Slovenia, a relatively small country situated in the western part of the Balkan Peninsula, with an
area of 20,273 km2, a relatively high species number is known (219 species). Species numbers of
countries occupying quite similar areas may differ substantially, as for example 590 gall midge
species are known to occur in the Czech Republic with an area of 78,900 km2 (Skuhravá 2006b),
283 species in Serbia with an area of 77,500 km2 (Simova-Tošić et al. 2000) and only 87 species
in Ireland with an area 70,280 km2 (O’Connor et al. 1999).
Species richness of countries in Europe is importantly influenced by the level of knowledge,
by the number of researchers who contributed to increasing known species numbers in the past
and also by the level of recent research. Germany, France, United Kingdom and other countries
given in the upper part of Table 3 are countries where investigations of gall midges have a long
tradition and where many researchers contributed to the high level of knowledge of this group.
On the other hand, Albania, Finland, Ireland and Norway may be counted as countries where
gall midge faunas are poorly known and only a few researchers have investigated gall midges.
In Belarus and Moldova gall midges are very poorly known. Lestremiinae and Porricondylinae
of Estonia are well known, in contrast to Cecidomyiinae the number of which are not known to
us at present.
An important measurement for evaluating of species numbers of areas under study is the
average species number per locality. It may be calculated for a particular area of the country
where investigations were carried out at particular number of localities and gall midge galls were
collected by the time and area unit collection method. The average species number per locality may
be calculated according to the formula: ASN=sf/nl, where ASN is the average species number per
locality, sf is the total of all species found at all examined localities in the course of investigati-
ons in this area and nl is the number of localities where investigations were carried out. Average
species numbers of Cecidomyiidae in countries of Europe where investigations of present authors
Fig. 5. Biological groups of gall midges of the family Cecidomyiidae in Europe.
100
have been done are shown in Fig. 7. The highest value of average gall midge species numbers
was found in central and western Europe. In central Europe the highest value was calculated for
Hungary (29 species) and the Czech Republic (26), in western Europe for central France (28
species) and south-eastern France (25). This fact may be conditioned or resulted from the highly
Table 3. Species numbers of Cecidomyiidae related to country area and evaluation of the level of knowledge and recent
research. For distribution of the Cecidomyiidae in three subfamilies see Table 1
country country area (km2) number of level of level of recent
species knowledge research
Russia (European) 3,960,000 650 medium few
Ukraine 603,700 300 medium many
France 547,030 668 very good many
Spain 505,992 229 medium few
Sweden 449,964 378 good few
Norway 385,155 170 poor few
Germany 357,050 836 very good many
Finland 338,145 135 poor no
Poland 312,685 463 very good many
Italy 301,318 508 very good many
United Kingdom 244,820 620 very good many
Romania 238,392 315 medium no
Belarus 207,600 38 poor no
Greece 131,940 211 good many
Bulgaria 110,910 240 good few
Iceland 103,000 0 unknown no
Hungary 93,030 332 very good few
Portugal 91,568 122 medium no
Austria 83,858 396 very good few
Czech Republic 78,866 590 very good few
Serbia 77,474 283 good many
Ireland 70,280 87 poor few
Lithuania 65,200 224 medium many
Latvia 64,589 506 very good many
Croatia 56,542 232 good many
Bosnia and Herzegovina 51,129 169 good many
Slovakia 48,845 362 very good few
Estonia* 45,226 93 see the note*
Denmark 43,094 307 good few
Netherlands 41,526 340 very good few
Switzerland 41,290 273 very good few
Moldova 33,843 8 very poor no
Belgium 30,510 140 medium few
Albania 28,748 19 poor no
Macedonia 25,333 148 medium many
Slovenia 20,273 219 good many
Montenegro 13,812 85 medium few
Cyprus 9,251 32 good no
Luxembourg 2,586 75 medium few
Andorra 468 30 good no
Malta 316 36 good no
Liechtenstein 160 65 good no
* Note. Estonia: Level of knowledge: medium for Lestremiinae and Porricondylinae, unknown for Cecidomyiinae; no
investigations of the subfamily Cecidomyiinae have been done.
101
varied topography and ecology of these parts of Europe. Many varied factors influence the bi-
odiversity of organisms, both plants and animals. Central Europe has heterogeneous geological
substrata and considerable differences in composition of natural vegetation. In addition, Central
Europe is situated at the crossroads of routes of plant species that penetrate to this part from all
directions, viz. from southern and northern Europe, from western and eastern parts. The average
species numbers decreases to the north and also to the south of Europe. In the northern part of
the Scandinavian Peninsula the average species number was found to be from 1 to 5, in southern
parts of Europe, and in some islands in the Mediterranean (Corsica, Crete, Mallorca) the average
species number is around 9, in Malta 4.5 and in Cyprus 3 species.
In Table 4 the countries of Europe are arranged according to the present species numbers
and these numbers are compared with data obtained 25 years ago during the preparation of the
section on the family Cecidomyiidae for the Catalogue of Palaearctic Diptera (Skuhravá 1986,
Skuhravá et al. 1984).
At present, Germany is the country with the highest species number, followed by France, Eu-
ropean part of Russia, United Kingdom, Czech Republic, Italy, Latvia and Poland. Seven other
countries (Austria, Sweden, Slovakia, the Netherlands, Hungary, Romania, Denmark) have a re-
lative high species numbers from 307 to 396 species, nine countries (Ukraine, Serbia, Bulgaria,
Switzerland, Croatia, Spain, Lithuania, Slovenia and Greece) have medium species number from
211 to 298 species, six other countries (Norway, Bosnia and Herzegovina, Macedonia, Belgium,
Finland and Portugal) are species poor having from 122 to 170 species and the remaining countries
characterized by decreasing species numbers from 93 to 11 per country may be considered to be
species poor within the framework of Europe. It is clear that it is necessary to include into the
evaluation of species numbers not only simple species numbers but also other criteria.
We included in evaluation of species numbers of Europe also the historical aspect. We com-
pared species numbers of countries in Europe and their changes during the last 25 years (Table 4).
Fig. 6. Biological groups of gall midges belonging to the subfamily Cecidomyiinae in Europe.
102
Additions of recorded species are expressed in percentages of the species numbers given in 1984.
Greece and Cyprus are two countries with the highest additional species numbers during the period
1984–2009. Greece was the country where only 19 species were known in 1984. All species were
discovered only by chance. In 1994 we started our systematic faunal investigations at localities
Table 4. Species numbers of Cecidomyiidae in Europe in 2009 and comparison with species numbers known in 1984
country number of species number of species change
1984 2009 1984–2009 [%]
1 Germany1 586, 406 836 21
2 France 523 668 28
3 Russia (European Part)2 524 650 24
4 United Kingdom 603 620 3
5 Czech Republic 504 590 17
6 Italy 334 508 52
7 Latvia 506
8 Poland 360 463 29
9 Austria 256 396 55
10 Sweden 261 378 45
11 Slovakia 350 362 3.5
12 Netherlands 295 340 15
13 Hungary 240 332 38
14 Romania 294 315 7
15 Denmark 160 307 92
16 Ukraine 298
17 former Yugoslavia3 287 400 39
18 Serbia 283
19 Bulgaria 104 240 130
20 Switzerland 81 237 192
21 Croatia 232
22 Spain 80 229 186
23 Lithuania 224
24 Slovenia 219
25 Greece 19 211 1000
26 Norway 65 170 162
27 Bosnia and Herzegovina 169
28 Macedonia 148
29 Belgium 89 140 57
30 Finland 135 135 0
31 Portugal 118 122 3
32 Estonia 93
33 Ireland 87
34 Montenegro 85
35 Turkey 34 70 105
36 Liechtenstein 65
37 Belarus 38
38 Malta 36
39 Andorra 30
40 Cyprus 9 32 255
41 Albania 11 19 72
Notes: 1) In 1984 the German Federal Republic included 586 species and the German Democratic Republic 406 species;
2) In 1984 the European part of the Soviet Union was formed of the following parts using the recent country names: Russia,
Ukraine, Belarus, Moldova, Estonia, Latvia, Lithuania; each of them is now an independent country;
3) The former Yugoslavia is formed at present of six independent countries: Bosnia and Herzegovina, Croatia, Macedonia,
Montenegro, Serbia, Slovenia.
103
spread over the whole of Greece and on several islands. In the course of several years we raised
species number to 211 species, i.e. more than ten times (1000%). Only nine species were known
in Cyprus in 1984. After our investigations the species number increased to 32 species (an increase
of 255%). Bulgaria, Switzerland, Spain, Norway and Denmark are countries where the progress
in investigations of gall midges is expressed in increasing species numbers from 90 to 200%.
Other countries with lower increasing additional species during this time period usually posses
a relatively high species number that were gathered mainly in previous time periods. The species
number of Finland remains at the same level as before 25 years.
Species density
Species density refers to the number of species per unit area. We use this term for the number of
gall midge species calculated for each country or island per unit of 1000 km2, that is for a square
with four equal sides each long 31.62 km. This method makes it possible to compare species
numbers occurring in various parts of Europe, determine where the area or areas with the highest
species numbers occur and to elucidate reasons that cause inequalities in distribution of species
numbers in Europe.
Species density for gall midge species occurring per 1000 km2 may be calculated using the
formula of MacArthur & Wilson (1967): S = x/a0.25 where S is the number of species per area of
Figs. 7, 8. Evaluation of gall midge species richness. 7 (left) – average species numbers of the family Cecidomyiidae
in countries of Europe where systematic faunal investigations have been made during 1955–2009. 8 (right) species
density of gall-inducing and plant-inhabiting species of the family Cecidomyiidae in Europe calculated per unit area of
1000 km2 for each country and island.
7
8
104
Table 5. Species density of gall-inducing and plant-inhabiting members of the subfamily Cecidomyiinae in countries
and islands of Europe
country or island area (km2) n species species density per 1000 km2
Albania 28,748 19 8.2
Andorra 468 30 37.5
Austria 83,858 352 116.5
Belgium 30,510 130 55.3
Bosnia and Herzegovina 51,129 169 63.3
Bulgaria 110,910 240 74.1
Canary Islands (Spain) 7,273 3 1.9
Corfu (Greece) 592 49 56.3
Corsica (France) 8,680 60 35.1
Crete (Greece) 8,260 38 22.3
Croatia 56,542 232 84.7
Cyprus 9,251 32 18.3
Czech Republic 78,866 564 189.2
Denmark 43,094 275 107.4
Faroe Islands (Denmark) 1,399 5 4.6
Finland 336,593 104 24.2
France 547,030 581 120.3
Germany 357,021 653 150.5
Greece 131,940 211 62.1
Hungary 93,030 332 107.1
Ireland 70,280 87 29.0
Italy 301,230 471 114.9
Italy, South Tyrol 7,400 312 189.1
Latvia 64,589 264 94.1
Liechtenstein 160 65 103.0
Lithuania 65,200 164 57.7
Luxembourg 2,586 75 57.7
Macedonia 25,333 148 66.1
Madeira (Portugal) 740 18 21.7
Mallorca (Spain) 3,411 33 24.4
Malta 316 36 48.6
Moldova 33,843 5 2.1
Montenegro 13,812 85 44.7
Netherlands 41,524 305 120.1
Norway 324,220 112 26.4
Poland 312,685 397 94.5
Portugal 91,568 122 39.4
Romania 238,391 304 76.0
Russia (European) 3,960,000 400 50.6
Samos (Greece) 479 34 42.5
Sardinia (Italy) 23,813 44 20.0
Serbia 88,361 283 91.3
Sicily (Italy) 25,426 89 40.1
Slovakia 48,845 355 134.5
Slovenia 20,273 219 104.2
Spain 504,851 212 42.9
Sweden 449,964 266 46.0
Switzerland 41,290 228 90.1
Ukraine 603,700 166 33.8
United Kingdom (GB) 244,820 526 132.8
105
1000 km2, x is the number of gall midge species found in the country and a is the whole area of
the country expressed in 1000 km2.
Results and calculations are given in Tables 5, 6 and in Fig. 8. Only countries of Europe whe-
re investigations were carried out or the summary of knowledge is available are given. Species
numbers in the third column involves only the species of the subfamily Cecidomyiinae includ-
ing gall-inducing and plant-inhabiting gall midges and inquilines, not the species of subfamilies
Lestremiinae and Porricondylinae, larvae of which do not induce galls.
On the basis of our calculations, two countries situated in Central Europe, the Czech Republic
and South Tyrol, the autonomous province in northern Italy, have the highest species density, each
with 189 gall midge species occurring per 1000 km2. Germany with 150 species in an area of
1000 km2 is at third place. United Kingdom, France, the Netherlands, situated in western Europe,
and Slovakia in Central Europe, also have a high level of species density, including 120–150 species
per area of 1000 km2. The countries of Central and western Europe have a higher species density
than the countries situated to the north and to the south. The very low species density have been
recorded in countries situated in northern Europe, viz. Finland, Norway, Sweden, and in the Faroe
Islands, situated in the Atlantic Ocean far from the European continent, and on the other hand the
countries and islands in southern Europe, viz. Madeira, Sardinia, Crete and Cyprus.
Species richness of gall midges in Europe is influenced by many factors. Above all by the
geographic position on the continent with different natural conditions of the realm. The number
of gall midges is much lower in the tundra and taiga covered with species-poor vegetation. In
countries of northern Europe, i.e. in Finland, Sweden and Norway, the relatively low gall midge
species number is the result of lower occurrence and poorer species composition of plants. In
temperate parts of Europe, i.e. in United Kingdom, Germany, France, Czech Republic, Slovakia,
Poland, Hungary, Romania and countries of the former Yugoslavia (Bosnia-Herzegovina, Croatia,
Serbia, Slovenia, Macedonia, Montenegro) broad-leaved and mixed forests cover large areas and
these forests contain many plant species which may be hosts of gall midges.
Table 6. Evaluation of gall-inducing and plant-inhabiting species of the family Cecidomyiinae occurring in countries of
Europe into five density groups according to the species density
density groups
very high high medium low very low
150 and more species 120–150 species 60–120 species 30–60 species 1–30 species
Czech Republic France Austria Andorra Albania
South Tyrol Netherlands Denmark Belgium Canary Is.
Germany Slovakia Hungary Corfu Crete
United Kingdom Italy Corsica Cyprus
Latvia Lithuania Faroe Islands
Liechtenstein Luxembourg Finland
Poland Malta Ireland
Serbia Montenegro Madeira
Slovenia Portugal Mallorca
Switzerland Samos Moldova
Bosna and Herzegovina Sicily Norway
Bulgaria Spain Sardinia
Croatia Sweden Belarus
Greece Ukraine
Macedonia
Romania
Russia
106
Species numbers per 1000 km2 in the southern parts of Europe, the so called Mediterranean
subregion, including southern parts of Greece, southern parts of Italy, southern part of the Iberi-
an Peninsula and islands in the Mediterranean Sea, are much lower than in Central Europe. For
example, the total value of species density for nine islands in the Mediterranean Sea is seven. Large
parts of these countries and islands were deforested in ancient times and at present the landscape
is covered mainly with sclerophyll vegetation (garrigue or maquis). Relations between plants
bearing galls to plants without galls are from 1:50 up to 1:80. We can confirm that low numbers
of galls occurs in these areas on the basis of our own experience. During our investigations when
we used the time-area collecting method, we could speak about a success when we found 5 to
10 galls of gall midges at one locality, whereas in Central Europe we usually found galls of 15
to 30 species at one locality.
Species richness of a country, zoogeographic region, continent or their parts is expressively
influenced by the level of knowledge and degree of exploration of such area. Germany, France,
United Kingdom, Italy, Poland, Czech Republic and Austria are countries with a relative long tra-
dition in the study of gall midges and with many researchers who devoted their efforts to the study
of gall midges and their galls in the past. These countries have also the highest species numbers
of gall midges. On the other hand there are many countries where the study of gall midges does
not have so long a tradition or is in the initial phase.
Gall midge species numbers in Greece, South Tyrol and Austria were relatively low before
our investigations. Only 20 gall midge species were known from Greece before 1994. After our
exploration the species number increased to 210. In South Tyrol the species number increased
from 24 to 312 and in Austria from 170 to 396. The number of gall midge species in Greece and
South Tyrol increased more than ten times after using the time-area collecting method.
Surprising is the high abundance of gall midges in Kazakhstan. Fedotova (2000) gave 804 gall
midge species occurring on the area of 2,780,000 km2 where the exploration was made at more
than 60 localities. Kazakhstan with 112 gall midge species occurring in the area unit per 1000 km2
is one of the very well explored countries in Central Asia, the western part of which is adjacent
to eastern Europe. Richness of gall midge species in that area is connected with relatively species
rich vegetation. The flora of Kazakhstan includes about 6000 plant species in 1118 genera and
161 families (Ryabushkina et al. 2008).
If we compare the species density of Europe with other parts of the Palaearctic region, species richness of the family
Cecidomyiidae in the East Palaearctic Region is known mainly owing to the studies of Yukawa (1971). He treated in his
revision 167 named and 17 unnamed gall midge species, forming a collection of 184 gall-inducing species of the family
Cecidomyiidae. After twenty five years of intensive studies Yukawa and his students (so called Yukawa’s Cecidological
School) were able to broaden the knowledge of Cecidomyiidae in Japan and to increase the species number from 184 to
628 (which is the number of sorts of galls caused by gall midges, including described and undescribed species), that is
3.4 times (Yukawa & Masuda 1996, Paik et al. 2004). Japan extending over an area of 377,835 km2 in the temperate to
subtropical zones of the East Palaearctic, is of quite similar size to Norway in the West Palaearctic where only 170 gall
midge species were found. In contrast, Norway is situated in the boreal part of northern Europe. Its northernmost part
has a mostly maritime subarctic climate and arctic tundra with species poor vegetation that does not give enough host
plants for gall midges.
Also of interest is the comparison of species numbers found in Europe with species richness of gall midges occurring
in North America. It occupies a territory of 24,490,000 km2, of which the USA has an area of 9,400,000 km2 and Canada
9,976,139 km2. Gagné (1989) in his book gives 891 gall midge species associated with 350 plant genera of 87 plant
families. If we count relations between gall midge species number known and the territory according to the formula of
MacArthur and Wilson, we obtain an average of 76 gall midge species per 1000 km2.
Species richness of the main genera
Numbers of species assigned to the genera of gall-inducing gall midges differ in the countries of
western and eastern Europe. In Table 7 we give species numbers of twelve of the most species-
107
Figs. 9–12. Distribution of species of the main genera of the family Cecidomyiidae in countries of Europe. 9 – Dasineura
Rondani, 1840. 10 – Contarinia Rondani, 1860. 11 – Asphondylia Loew, 1850. 12 – Rhopalomyia Rübsaamen, 1892.
910
11 12
108
-rich genera of the world and compare these numbers with numbers in the Palaearctic, Western
and Eastern Europe and in Kazakhstan, situated in south-western Asia, the area of which is greater
than western Europe.
Dasineura is the largest genus of the family Cecidomyiidae containing 490 species spread
over all the world. Most of these species – 335 – occur in the Palaearctic Region, 112 species in
the Nearctic Region and only a few species in other biogeographic regions. Larvae induce galls
mainly on leaves, on leaf and flower buds on host plants of various plant families. In Europe
most species are associated with Fabaceae, Rosaceae, Asteracae, Brassicaceae and Lamiaceae.
Dasineura is the most species-rich genus in the Palaearctic Region and is abundant in Western
Europe where 230 species occur. The species number is much lower in Eastern Europe (Fig. 9).
In Kazakhstan it is also the most species-rich genus and is in first position, together with the
genus Halodiplosis.
Contarinia with 340 species described in the world is in second place. In Western Europe
135 species were found. Larvae induce galls mainly on flowers, flower and leaf buds and leaves
or live freely in flower heads of many host plants of various plant families. In Europe most spe-
cies are associated with Fabaceae, Asteraceae and Poaceae. Species are abundant in Western and
Central Europe, their number decreases to the east, southeast and southwest but they are relati-
vely abundant in Kazakhstan. Of 230 species that are distributed mainly in Central Europe, the
highest species numbers are found in Germany, Czech Republic, France and United Kingdom in
the latitudinal belt between 350 and 540 North. Lower species numbers were found in Norway,
Sweden and Finland and, on the other hand, species are relatively abundant in eastern parts of
southern Europe (Fig. 10).
Asphondylia with 270 species occurring in the world is in third place. Of these, 50 species
occur in Central and Western Europe (Fig. 11). Species number decreases to the south and east. In
Kazakhstan only nine species were found. Larvae induce galls on floweror leaf budsand fruits on
host plants of various plant families. Galls are usually associated with fungal mycelia (so called
ambrosia galls). In Europe the galls are induced on host plants belonging mainly to Fabaceae
and Lamiaceae. Asphondylia is considered to have its origin in the Neotropical Region and then
to have spread throughout the world (Möhn 1961, Tokuda & Yukawa 2007). We suppose that at
least one centre of the origin of the genus Asphondylia is in the Mediterranean area in southern
Europe in the western part of the Palaearctic Region. This area is considered to be one of the cen-
Table 7. Species numbers of the main genera of gall-inducing Cecidomyiinae in the world, in the Palaearctic Region,
Western and Eastern Europe in comparison with Kazakhstan (Central Asia)
genus World Palaearctic Europe Kazakhstan
Western Eastern
Dasineura Rondani, 1840 490 335 230 61 92
Contarinia Rondani, 1860 340 225 135 42 79
Asphondylia Loew, 1850 270 66 50 20 9
Rhopalomyia Rübsaamen, 1892 260 161 38 9 60
Lasioptera Meigen, 1818 125 50 27 9 3
Stefaniola Kieffer, 1913 108 108 6 0 74
Rabdophaga Westwood, 1847 80 40 40 18 11
Jaapiella Rübsaamen, 1915 80 80 35 9 51
Resseliella Seitner, 1906 47 27 23 9 1
Macrolabis Kieffer, 1892 50 50 35 5 22
Baldratia Kieffer, 1897 38 36 3 1 20
Mayetiola Kieffer, 1896 31 30 28 1 1
109
tres of origin of plant and animal species in Europe. In this area 50 described species and several
undescribed species of the genus Asphondylia are distributed which are associated with 13 plant
families. Interestingly, most species of this genus are associated with herbaceous plants, only
a few with trees and shrubs. No species have been found in Norway and Finland and the species
numbers in northern parts of Europe are low. Species of the genus Asphondylia occur abundantly
in southern Europe. This fact supports our hypothesis that at least one of the centres of diversity
of the genus Asphondylia is situated in Europe. In the Fig. 21 there are shown distribution areas
of several species of this genus.
Rhopalomyia, including 260 species in the world, is relatively species-rich in central, southeast
and western Europe where it contains 38 species (Fig. 12). Its number decreases markedly to the
south. No species were found in the islands of the Mediterranean Sea. Many Rhopalomyia species
were found and occur in Central Asia, mainly in Kazakhstan. Larvae induce galls on stems, buds
and leaves of host plants mainly of the family Asteraceae. Galls often occur on several organs
of the same host plant species. Alternation of plant organs is connected with the development of
several generations per year.
The genus Lasioptera includes 50 species in the Palaearctic Region and 27 of them occur in
Western Europe (Fig. 13). Larvae induce galls on stems of host plants of various families, mainly
on Poaceae and Apiaceae, or develop in fruits without making galls. Galls are usually associated
with fungal mycelia (so called ambrosia galls). Larvae of Lasioptera buhri develop in stems of
host plants belonging to several genera of three different families. Species of the genus Lasioptera
are relatively abundant in Central and Western Europe and numbers decreases northwards and
southwards. Also in Central Asia its numbers are low – only three species occur in Kazakhstan.
Stefaniola contains 108 species and is a Palaearctic genus. Species are distributed in Central
Asia, mainly in Kazakhstan and adjacent countries, and in North Africa. Only six species reach
to Europe where they occur in southwestern parts, in Spain and Portugal (five species) and in
Italy (one species), all very rare. Larvae induce leaf and bud galls on various species of Che-
nopodiaceae. Four species are associated with Salsola vermiculata, viz. Stefaniola bilobata, S.
gloma, S. parva and S. salsolae, S. vastita cause galls on Anabasis. All these species occur in the
Iberian Peninsula. Stefaniola mediterranea, causing galls on stems of Salicornia europaea and
Halocnemum strobilaceum, was found in Italy (Fig. 14).
Rabdophaga is a Holarctic genus with 40 species occurring in the Palaearctic Region and with
the same species number occurring in North America. Larvae cause stem, bud and leaf galls on
various species of Salix and one species, Rabdophaga giraudiana, is known to be associated with
Populus tremula and P. alba. Both genera of host plants belong to the family Salicaceae. The
species are abundant in central and northern parts of Western Europe and their number decreases
to the south and southwest (Fig. 15). Only one species was found in Sardinia and Mallorca in the
Mediterranean and no species was found in the remaining seven islands in the Mediterranean.
a relatively low species number was found in Kazakhstan.
Jaapiella is a Palaearctic genus with 80 species of which 35 species occur in Western Europe
(Fig. 16). Larvae induce galls on leaf and flower buds and leaves of host plants of various plant
families. Some species are inquilines in galls of other gall midges. Higher species numbers occur
in Central and Western Europe and species numbers reduces towards the marginal parts of Europe.
Only a few species were found in northern and southern Europe, on islands in the Mediterranean
and no species was found in Mallorca in the Mediterranean Sea. a relatively large number of
species occurs in Kazakhstan.
Macrolabis is also a Palaearctic genus with 35 species distributed in Western Europe (Fig. 17).
Larvae induce galls on leaf and flower buds on host plants of various families. About one half
of species are inquilines in galls of other gall midges. Species numbers decrease from Central
110
Figs. 13–16. Distribution of species of the main genera of the family Cecidomyiidae in countries of Europe. 13 – Lasioptera
Meigen, 1818. 14 – Stefaniola Kieffer, 1913. 15 – Rabdophaga Westwood, 1847. 16 – Jaapiella Rübsaamen, 1915.
13 14
15 16
111
and Western Europe to the south and no species was found in Macedonia and Montenegro in the
Balkan Peninsula and in the islands in the Mediterranean, with the exception of Corsica. Species
of this genus were found abundantly in Kazakhstan.
Baldratia is a Palaearctic genus with 36 species and with two species occurring in Africa. Larvae
induce galls on stems of various Chenopodiaceae in Central Asia and only three species occur in
Western Europe. Only one species, Baldratia salicorniae, causing galls on Salicornia fruticosa,
is native to Europe and occurs scattered along the coast of the Black Sea, along the coasts of
the Mediterranean Sea and in several islands in this sea. Galls of B. salicorniae were found also
at several localities in southern France, Spain, Portugal and in southern parts of England on the
coast of the Atlantic Ocean. Baldratia suaedae and B. similis are species which have their origin
in the Middle East. Galls of Baldratia suaedae on Suaeda vera, described from material found in
Israel, were discovered at two localities in Europe, viz. on the Canary Islands and in Monegros in
north-eastern Spain. Galls of Baldratia similis causing galls on Anabasis aphylla, described from
material found in Iran, were found at one locality in south-eastern Russia (Fig. 18).
Mayetiola is a Palaearctic genus containing 30 species with only one species native to North
America. Larvae induce galls on stems of various species and genera of Poaceae. Mayetiola de-
structor, a serious pest of cereals that occurred abundantly in Europe in the past, is considered to
have its origin in south-eastern Europe, probably in the Ukraine. It has been accidentally introduced
with cereals into other biogeographic regions where it causes serious damage. Most species were
described from western Europe, only one species occurs in eastern Europe and in Kazakhstan.
Species of this genus occur abundantly in Central and Western Europe, their number reduces
northwards and southwards and no species were found in Croatia and Slovenia in the Balkan Pe-
ninsula or on seven islands in the Mediterranean. Mayetiola destructor is the only species known
to occur in Sardinia and Malta. It has been probably introduced there with cereals (Fig. 19).
Resseliella is a genus with cosmopolitan distribution and diverse biology. Of 43 species occur-
ring in the Holarctic, 27 occur in the Palaearctic and 16 in the Nearctic region. Larvae of many
Palaearctic species live under the bark of trees and shrubs, causing them damage, and some species
are considered to be pests. Several species are associated with resin of coniferous trees or with
cambium liquid flowing from stems of young broad-leaved trees that were primarily wounded
Table 8. Distribution of species of the family Cecidomyiidae occurring in Europe and in zoogeographical units of the
world
taxon zoogeographical unit
European Euro- Mediter- Palaearctic Holarctic cosmopolitan alien
siberian ranean
Cecidomyiidae
(1800 species) 1278 216 170 25 81 7 23
% 71.0 12.0 9.5 1.3 4.5 0.4 1.3
Lestremiinae
(280 species) 181 54 0 0 43 2 0
% 64.6 19.3 15.4 0.7
Porricondylinae
(310 species) 280 12 0 5 13 0 0
% 90.3 3.9 1.6 4.2
Cecidomyiinae
(1210 species) 817 150 170 20 25 5 23
% 67.5 12.5 14.0 1.7 2.0 0.4 1.9
112
Figs. 17–20. Distribution of species of the main genera of the family Cecidomyiidae in countries of Europe. 17 Macrolabis
Kieffer, 1892. 18 – Baldratia Kieffer, 1897. 19 – Mayetiola Kieffer, 1896. 20 – Resseliella Seitner, 1906.
17 18
19 20
113
by animals (Dengler 2004). European species are associated with 11 plant families: six species
with Pinaceae and four with Rosaceae, other families each hosting one gall midge species. The
biology of several species remains unknown. Most species are distributed in Central and Western
Europe, their number decreases in southern Europe and no species was found in Mallorca, Corsica
and Sardinia and Cyprus (Fig. 20).
Geographic distribution
The gall midge species occurring in Europe may be divided, according to their overall distribution
in the world, into six zoogeographic units: European, Eurosiberian, Mediterranean (including
Submediterranean), Palaearctic or Euroasian, Holarctic and cosmopolitan (Table 8). In addition,
species that penetrated into Europe from other continents and are members of the present European
Fig. 21. Distribution areas of five species of the genus Asphondylia Loew, 1850 in Europe shown by lines of their limits:
A. calycotomae Kieffer, 1912 causing galls on Calycotome spinosa (Fabaceae) (blue line); A. melanopus Kieffer, 1890
inducing galls on Lotus corniculatus (Fabaceae) (red line); A. punica Marchal, 1897 evoking galls on Atriplex halimus
(Chenopodiaceae) (brown line); A. sarothamni (Loew, 1850) producing galls on Cytisus (Sarothamnus) scoparius
(Fabaceae) (green line); A. ulicis Trail, 1873 causing galls on Ulex europaeus (Fabaceae) (yellow line). A. calycotomae
and A. punica are Mediterranean species, A. ulicis is an Atlantic species, A. sarothamni is a sub-Atlantic species and A.
melanopus a European species.
114
gall midge fauna are designated as alien. On the other hand, some European gall midge species
that spread into other continents are considered to be immigrants there and some European gall
midge species were introduced in other continents of the world as agents for biological control
of pests or of weeds. The distribution of species of the subfamily Cecidomyiinae including the
gall-causing and plant inhabiting species is better known than the distribution of species belonging
to subfamilies Lestremiinae and Porricondylinae that require different sampling methods.
Fig. 22. Distribution area of Mikiola fagi (Hartig, 1839) in countries of Europe including its occurrence in single countries
(black circles) and its absence (white circles), and distribution area of its host plant, Fagus sylvatica L. (Fagaceae) (black
line). Distribution area of the host plant after Meusel et al. (1965–1992).
115
Of 1800 species of the family Cecidomyiidae forming the present fauna of Europe, 71% are
European, 12% Eurosiberian, 9.5% Mediterranean and Submediterranean, 4.5% Holarctic, 1.3%
Palaearctic, 0.4% cosmopolitan and 1.3% alien species. In the best known group of gall midges,
in the subfamily Cecidomyiinae, we found all types of distribution. Of interest is the fact that in
the subfamilies Lestremiinae and Porricondylinae there were not found gall midge species with
Mediterranean or Submediterranean types of distribution and only a few European species occur
or have been found beyond the boundary of Europe, in Asia or in North America.
European species occur only in Europe and are considered to have the centres of their origin
in Europe. Altogether 1278 species (71%) of the family Cecidomyiidae known to occur in Europe
belong in this group, i.e. nearly three quarters of all species. Areas of their distribution may range
from very small to large. Most of them are known only from the type locality in some country of
Europe and have never been recorded again after the original description. Several species have
small areas of distribution, occurring only in the country where they were discovered and in one or
two adjacent countries. Some species occur abundantly in several countries of Central Europe and
some of them extend southwards to the Mediterranean and even to North Africa, others extend to
south-east or to western Turkey or the Caucasus. Typical representatives of European gall midges
are Mikiola fagi galling leaves of Fagus sylvatica (Fig. 22), Macrodiplosis pustularis with galls
on leaves of Quercus robur and its relatives, Acericecis vitrina causing galls on leaves of Acer
pseudoplatanus, Zygiobia carpini inducing galls on leaves of Carpinus betulus, and Taxomyia
taxi causing galls on buds of Taxus baccata. Most species of the subfamily Porricondylinae and
about two thirds of species of the subfamily Lestremiinae have European distributions.
Several gall midge species that are members of the European fauna have a particular or
strange distribution area. Gall midge species associated with Cytisus (Sarothamnus) scoparius,
Fig. 23. Distribution area of Kochiomyia kochiae (Kieffer, 1909) (black circles) on Bassia prostrata (L.) Scott (= Kochia
prostrata (L.) Schrad.) (Chenopodiaceae) (black line), a Pontic-Pannonian species. Distribution area of the host plant
after Meusel et al. (1965–1992).
116
viz. Asphondylia sarothamni, Contarinia scoparii, Dasineura tubicoloides, Jaapiella sarothamni
and Janetiella tuberculi, are European and sub-Atlantic species occurring abundantly along the
shores of the Atlantic Ocean, penetrating inland and reaching, with their host plant, eastwards to
the Czech Republic. Kochiomyia kochiae is a Pontic-Pannonian species causing galls on Bassia
prostrata (= Kochia prostrata) (Fig. 23). It occurs abundantly along the shores of the Black Sea
(Pontus Euxinus) and in the Pannonian lowlands in Hungary (Skuhravá & Skuhravý 1999). The
galls were found also in southern France and in north-eastern Spain where this species reaches the
Fig. 24. Disjunct area of distribution of Jaapiella alpina (Löw, 1877) (black circles) and its host plant Silene acaulis (L.)
Jacq. (Caryophyllaceae) (black line) in Europe. Distribution area of the host plant after Meusel et al. (1965–1992).
117
most western limits of its remarkable distribution area. The gall midge Jaapiella alpina causing
galls on Silene acaulis, the host plant species of typical arctic-alpine distribution, has a disjunct
distribution area with scattered occurrence at very high elevations in the mountains of Europe
(Fig. 24).
Eurosiberian species inhabit the Eurosiberian subregion of the Palaearctic region. About one
eighth, i.e. 216 species (12%) of the Cecidomyiidae known to occur in Europe belong in this
group. They have centres of origin in Europe where they occur usually abundantly and extend at
least to Western Siberia, with some of them reaching to Central Siberia and only few reaching
to Eastern Siberia and to the most eastern part of the Palaearctic Region, to the Far East. Typical
representatives of Eurosiberian species are Harmandiola cavernosa, H. globuli, H. populi causing
galls on leaves of Populus tremula, Lasioptera rubi inducing galls on stems of Rubus idaeus and
its relatives, Iteomyia capreae on Salix caprea (Fig. 26), Geocrypta galii on Galium mollugo and
Dasineura urticae on Urtica dioica. Thecodiplosis brachyntera galling needles of Pinus sylvestris
and Pinus mugo occurs abundantly in Central Europe where it is classed as a pest causing serious
outbreaks from time to time (Skuhravý 1991). Its occurrence decreases eastwards and the galls
were found in southern part of Central Siberia (Skuhravá & Skuhravý 1993b).
Mediterranean species have centres of origin in the Mediterranean area. About 170 species, i.e.
9.5% of the family Cecidomyiidae known to occur in Europe belong in this group. They occur along
the shores of the Mediterranean and are associated with Mediterranean host plant species. Some
of them occur over greater areas and a few species reach the northern limits of their distribution
Fig. 25. Mediterranean distribution area of Dasineura oleae (Angelini, 1831) (black circles) and its host plant, Olea
europaea L. (Oleaceae) (black line) in the southern part of Europe and westernmost Asia. Distribution area of the host
plant after Meusel et al. (1965–1992).
118
areas in Central Europe. In such case they are defined as Submediterranean species. Nine gall
midges associated with Quercus cerris, viz. Dryomyia circinans, Contarinia quercicola, C. subu-
lifex, Dasineura tubularis, Janetia cerris, J. homocera, J. nervicola, J. pustularis and J. szepligetii
that occur abundantly in the Mediterranean area reach the northern limits of their distribution in
the eastern part of Austria, southern part of the Czech Republic and of the Slovak Republic.
Typical Mediterranean species are Dasineura oleae inducing galls on leaves of Olea europaea
(Fig. 25), Phyllodiplosis cocciferae and Dryomyia cocciferae causing galls on leaves of Quercus
coccifera; four species associated with Quercus ilex, viz. Contarinia ilicis, C. luteola, Dasineura
ilicis and Dryomyia lichtensteinii; Dasineura asparagi causing galls on Asparagus aphyllus;
four species associated with Artemisia herba-alba, viz. Rhopalomyia hispanica, R. navasi, R.
producticeps and R. tavaresi; Braueriella phillyreae, Dasineura rufescens and Probruggmanniella
phillyreae which are associated with various species of Phillyrea. Also six gall midge species
associated with various Erica spp. have Mediterranean type distributions. Dasineura broteri,
D. elegans and D. zimmermanni occupy only small distribution areas. In contrast, Dasineura
ericaescopariae, Myricomyia mediterranea and Wachtliella ericina occupy larger areas in the
Mediterranean. W. ericina reaches up to southern England, to southern Denmark and to the
southern part of the Czech Republic in Central Europe. Asphondylia coronillae causing galls on
buds and pods of Coronilla emerus is a Mediterranean species that occurs abundantly in southern
Europe and penetrates up to Switzerland and northern Italy. Lasioptera eryngii causing large
galls on stems of Eryngium campestre occurs scattered in the whole Mediterranean and occupies
a large area reaching up to Turkey. It penetrates northwards up to the Czech and Slovak Republics
where the most northern boundary of its distribution area runs. It may be designated as a typical
Submediterranean species.
Palaearctic or Euro-Asian species are species that inhabit Europe or the Eurosiberian subregion
and at least one of the other Palaearctic subregions, i.e. Central Asian or East Palaearctic subregion.
Only about 25 species (1.3%) of the family Cecidomyiidae known to occur in Europe belong in
this group, mainly species caught as adults, viz. Trisopsis abdominalis, T. karelini, T. punctiven-
Fig. 26. Eurosiberian distribution area of Iteomyia capreae (Winnertz, 1853) (black circles) and its host plant, Salix
caprea L. (Salicaceae) (black line) including Europe, Siberia and the East-Palaearctic subregion. Distribution area of the
host plant after Meusel et al. (1965–1992).
119
tris, T. tyroglyphi, Stomatosema kamali of the subfamily Cecidomyiinae and Peromyia truncata
and Polyardis bispinosa of the subfamily Lestremiinae. Of gall-causing species of the subfamily
Cecidomyiinae, Etsuhoa sabinae and Xerephedromyia ustjurtensis, have disjunct Euro-Asian areas
of distribution. Galls of Etsuhoa sabinae on Juniperus sabina occur rarely in mountains of Europe
and were also found in mountains of eastern Kazakhstan. Galls of Xerephedromyia ustjurtensis on
Ephedra distachya were discovered in western Kazakhstan near the Caspian Sea, in Turkmenistan,
Jordan, in southern Ukraine, northern Spain and southern France and Italy. Such types of disjunct
distribution may be denominated as Mediterraneo-Turanian. Also Lasioptera umbelliferarum
causing galls on Hippomarathrum (formerly Seseli) has a disjunct distribution area. Galls were
found in Sicily (southern Italy), in southern Russia, Georgia, Azerbaijan, Iran and Israel.
Holarctic species occur simultaneously in the Palaearctic and in the Nearctic regions. 81 species
(4.5%) of the family Cecidomyiidae known to occur in Europe belong in this group. The most
abundant are the Lestremiinae with 43 species, followed by the Cecidomyiinae with 25 species
and at the last position are the Porricondylinae with only 13 species. Camptomyia multinoda and
Porricondyla nigripennis of the subfamily Porricondylinae, Aphidoletes aphidimyza, A. thompsoni
and A. urticaria, Coquillettomyia dentata and C. lobata, Mycodiplosis coniophaga and M. inimica
of the subfamily Cecidomyiinae may be considered to be truly Holarctic species. These species
are mycophagous or zoophagous and are not associated with specific host plants. On the other
hand, several gall midge species associated with their host plants, mainly with cereals, fruit trees
and fodder crops, that occur in both regions, may be classed as secondarily Holarctic because
their host plants are of European origin and gall midges were imported from Europe into North
America with their host plants. For example: Contarinia pyrivora and Dasineura pyri causing
galls on Pyrus communis; Dasineura mali on Pyrus malus (Fig. 28); Dasineura alopecuri devel-
oping in inflorescences ofAlopecurus pratensis; D. gentneri and D. leguminicola associated with
Fig. 27. Cosmopolitan distribution of the gall midge Lestremia cinerea Macquart, 1826 (black circles) in the biogeogra-
phical regions of the world: 1 – Palaearctic, 2 – Nearctic, 3 – Afrotropical, 4 – Indomalayan, 5 – Oceanian, 6 Australian,
7 – Neotropical, 8 – Antarctic regions.
120
Trifolium spp. In some cases it is not quite clear where a particular gall midge species is native
and to which part it was introduced.
Cosmopolitan species are species that occur on all continents of the Earth having a world-wide
distribution. Only seven species of the family Cecidomyiidae known to occur in Europe may be
assigned to this group: Anarete johnsoni, Lestremia cinerea (Fig. 27) and Monardia modesta (Les-
tremiinae), Didactylomyia longimana, Feltiella acarisuga, Stomatosema obscura and Silvestriola
cincta (Cecidomyiinae) were found on several continents and are considered to be cosmopolitan
in distribution. The origin of most of them is unknown. Mayetiola destructor developing on cere-
als is considered to be a primarily European species that has been imported into other continents
probably with straw.
Alien species (non-native, exotic, non-indigenous, foreign) are species introduced outside their
normal distribution. Invasive alien species are alien species whose establishment and spread
modify ecosystems, habitats, or species (DAISIE 2009). In the fauna of gall midges of Europe
23 species were found that are noted as alien or invasive species (Table 9). Most of them are
associated with various plant families and four species are predators. They were introduced into
Table 9. Alien gall midge species occurring in Europe, their host species, plant family and origin; zoophagous species are
marked by an asterisk before the species name
gall midge species host species plant family origin
Asphondylia buddleia Felt, 1935 Buddleia racemosa Loganiaceae North America
Clinodiplosis cattleyae (Molliard, 1903) Cattleia Orchidaceae Central and South
Americas
Contarinia citri Barnes, 1944 Citrus spp. Rutaceae Africa
Contarinia quinquenotata (Löw, 1888) Hemerocallis fulva Liliaceae temperate Asia
Dasineura gibsoni Felt, 1911 Cirsium Asteraceae North America
Dasineura gleditchiae (Osten Sacken, 1866) Gleditchia triacanthos Caesalpiniaceae North America
Dasineura oxycoccana (Smith, 1890) Vaccinium spp. Ericaceae North America
*Dicrodiplosis pseudococci (Felt, 1914) Planococcus citri Africa
(Pseudococcidae)
*Epidiplosis filifera (Nijveldt, 1965) Ceratoplates floridensis Eastern Asia
(Coccidae)
*Feltiella acarisuga (Vallot, 1827) Tetranychidae (Acari) unknown
Horidiplosis ficifolii Harris, 2003 Ficus benjamina Moraceae tropical Asia
Janetiella siskiyou Felt, 1917 Chamaecyparis Cupressaceae North America
lawsoniana
*Lestodiplosis aonidiellae Harris, 1968 Aonidiella aurantii Africa
(Diaspidae)
Obolodiplosis robiniae (Haldeman, 1847) Robinia pseudoacacia Fabaceae North America
Orseolia cynodontis Kieffer
et Massalongo, 1902 Cynodon dactylon Poaceae Africa
Procontarinia matteiana Kieffer
et Cecconi, 1906 Mangifera indica Anacardiaceae tropical Asia
Prodiplosis vaccinii (Felt, 1926) Vaccinium spp. Ericaceae North America
Prodiplosis violicola (Coquillett, 1900) Viola spp. Violaceae North America
Resseliella conicola (Foote, 1956) Picea sitchensis Pinaceae North America
Rhopalomyia chrysanthemi (Ahlberg, 1939) cultivated Asteraceae temperate Asia
Chrysanthemum
Rhopalomyia grossulariae Felt, 1911 Ribes grossularia Grossulariaceae North America
Stenodiplosis panici Plotnikov, 1926 Panicum spp. Poaceae temperate Asia
Stenodiplosis sorghicola (Coquillett, 1899) Sorghum spp. Poaceae Africa
121
Europe unintentionally from other parts of the world. Typical representatives are Obolodiplosis
robiniae causing galls on leaflets of Robinia pseudoacacia (Fig. 29), and Dasineura gleditchiae,
causing galls on leaflets ofGleditchia triacanthos, both originally Nearctic species that have been
imported into Europe unintentionally, probably with seedlings of their host plant. Ten species came
to Europe from North America, one species from Central and South America, six from Asia, five
from Africa and the origin of one species is unknown (Skuhravá et al. 2007, 2010).
Fig. 28. Distribution of Dasineura mali (Kieffer, 1904) (black circles) on apple trees Malus sylvestris Mill. and Malus
domestica Borkh. (Rosaceae) in Europe (black line). D. mali probably originates, as do its host plants, from southern
Europe and western Asia which are primary areas of its distribution, and it was imported secondarily to other parts of the
world. Distribution area of the host plant after Meusel et al. (1965–1992).
122
Five European gall midge species were intentionally introduced into other continents for bi-
ological control of weeds: Cystiphora sonchi against Sonchus arvensis in Canada (Peschken
1982); Cystiphora schmidti against skeleton weed (Chondrilla juncea) in Australia, California
and Argentina; Zeuxidiplosis giardi against St. John’s wort (Hypericum perforatum) in Hawaii,
New Zealand and Australia; Spurgia euphorbiae against leafy spurge (Euphorbia esula) in North
America (North Dakota) (Sobhian et al. 2000); Rhopalomyia tripleurospermi against scentless
chamomile (Tripleurospermum perforatum) in Canada (Skuhravá & Hinz 2000). On the other
hand, the European species Gephyraulus raphanistri which was tested as a potential control agent
of Raphanus raphanistrum, one of the most important weeds of crops in Australia, was found to
have unsuitable phenological characteristics (Vitou et al. 2008).
Endemic species form a special category. Such species are native to a particular geographical
region or their occurrence is restricted to such region. In Europe it is possible to class thirty eight
gall midge species as endemic. They are known so far only from the Iberian Peninsula. They
have not been recorded in any other country and seem to be restricted to the Iberian Peninsula. It
is necessary to emphasize that they may be revealed in some of other countries in the future. As
Fig. 29. Occurrence of Obolodiplosis robiniae (Haldeman, 1847) (black circles) causing galls on Robinia pseudoacacia
L. (Fabaceae) and its spread throughout Europe. O. robiniae is a Nearctic species, alien to Europe. It has been imported
into Europe, probably with seedlings, and its galls were discovered for the first time in 2003 in northern Italy. Since then
it has spread quickly over large areas of Europe up to Doneck in Ukraine in 2006, to southern England in 2007, northern
Spain and southern Sweden in 2008.
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a true endemic may be regarded only such species which are associated with host plants endemic
to the Iberian Peninsula, as for example Dasineura halimii and D. herminii causing galls on
Halimium spp. (Skuhravá et al. 2006).
We have prepared maps showing the distribution areas of more than 500 gall midge species.
Some of them were published in our articles and the larger part await publication in the future.
In addition, we have drawn several hundreds of maps showing the occurrence of gall midge spe-
cies in several countries of Europe where we summarized previous knowledge, i.e. of the Czech
Republic (Skuhravá 1994a, b), Slovakia (Skuhravá 1991), France (Skuhravá et al. 2005), Spain
and Portugal (Skuhravá et al. 2006), Poland (Skuhravá et al. 2008) and Austria (Skuhravá &
Skuhravý 2009a).
Geographic position and gradients
Gall midge species richness changes with composition of natural vegetation and with geographic
position, mainly along a north-south axis (Skuhravá & Skuhravý 1998). We tested both geogra-
phic gradients, latitudinal and longitudinal, using the average species numbers per locality
obtained from samples taken by the time unit area collection method at localities with precisely
determined geographic positions. Fundamental data for the analysis are given in Table 10 and
results are shown in Figs 30 and 31.
The occurrence of gall midges given by average species numbers along the latitudinal gradient
produces interesting results (Fig. 30). The average species numbers of gall-inducing Cecidomyiidae
Fig. 30. Average species numbers of gall-inducing and plant inhabiting species of the subfamily Cecidomyiinae in coun-
tries of Europe along the latitudinal gradient of 3800 km from the northernmost investigated area in northern Norway
(Harstad) to the southernmost investigated area in the island of Malta in the Mediterranean Sea. All samples have been
taken by the time and area unit collection method.
124
Table 10. European countries where systematic faunal investigations have been undertaken by the present authors during the period 1955–2009, important characte-
ristics of countries and average species numbers of Cecidomyiidae. Geographic coordinates (latitude and longitude) are related as far as it is possible to the area or
town situated nearest to the study area. Altitudes include the lowest and the highest elevations of examined localities. Biogeographic provinces are given according
to Udvardy (1975), types of natural vegetation according to Noirfalise (1987). At the end of the table there are added data obtained in the course of investigations in
the southern part of Central Siberia (Asia) for comparison with data obtained in Europe. ASN – average species number
country lat. N long. E altitude biogeographic provinces type of natural vegetation ASN references
m a.s.l.
Austria, Wien 48°12’ 16°22’ 240 Central European Highlands mixed forest, conifer forests 17.0 Skuhravá & Skuhravý 2009a
115–2500
Bulgaria, Sofia 42°40’ 23°19’ 1–2000 Balkan Highlands mixed forest, oak forest 14.0 Skuhravá et al. 1991
Bulgaria, Varna 43°13’ 27°55’ 1–180 Black Sea Coast Pontic beech forest 14.0 Skuhravá et al. 1991
Corfu (Greece) 39°37’ 20°02’ 1–250 Mediterranean Sclerophyll Hellenic oakwood 12.6 Skuhravá & Skuhravý 2006b
Corsica (France) 41°55’ 08°44’ 1–1000 Mediterranean sclerophyll 9.8 Skuhravá & Skuhravý (in prep.)
Crete (Greece) 35°20’ 28°08’ 1–800 Mediterranean sclerophyll 9.2 Skuhravá & Skuhravý 1997a
Cyprus 35°00’ 33°00’ 1–150 Mediterranean sclerophyll 3.1 Skuhravá & Skuhravý 2004a
Czech Republic, Prague 50°05’ 14°25’ 120–1603 Central European Highlands mixed forest 26.0 Skuhravá 1994a, b
Denmark, Sjæland 55°66’ 12°34’ 1–75 Atlantic Province
(Copenhagen) Boreo-nemoral beech forest 22.0 Skuhravá et al. 2006
Faroe Islands, Tórshavn 62°00’ 6°46’W 0–300 Arctic-Alpine blanket bogs 1.0 Skuhravá & Skuhravý 2009
(Denmark)
France, Orleans 47°54’ 01°54’ 110–630 Atlantic Province oak forest 28.0 Skuhravá & Skuhravý 2004d
France, Hautes Alpes,
Grenoble 45°10’ 05°43’ 850–2645 Central European Highlands beech-fir forest 25.0 Skuhravá & Skuhravý 2004c
Germany, Bayerischer 48°32’ 09°03’ 650–1450 Middle European Forest coniferous, mixed forest 13.0 Skuhravá & Skuhravý 1992b
Wald
Germany, Harz 51°41’ 10°58’ 450–550 Middle European Forest Hercynian beech forest 20.0 Skuhravá & Skuhravý 1988
Germany, Fichtelgebirge 50°07’ 12°00’ 528–875 Middle European Forest Hercynian beech forest 13.0 Skuhravá & Skuhravý 1992a
Greece, Athens 38°03’ 23°40’ 140 Balkan Highlands, oak forest, sclerophyll 9.3 Skuhravá & Skuhravý 1997a
1–1100 Mediterranean
Hungary, Budapest 47°30’ 19°04’ 116–1015 Pannonian Danubian thermophilous 29 Skuhravá & Skuhravý 1999
oak forest
Italy, Central part (Roma) 41°58’ 12°40’ 10–13 Mediterranean Quercus ilex forest 8.0 Skuhravá & Skuhravý (unpubl.)
Italy, Calabria, Cetraro 39°31’ 15°56’ 1–560 Mediterranean Quercus ilex forest 14.0 Skuhravá & Skuhravý (in prep.)
Italy, South Tyrol, Bolzano 46°20’ 11°14’ 224–2340 Central European Highlands spruce forest 15.0 Skuhravá & Skuhravý
2001–2009
Liechtenstein, Vaduz 47°07’ 09°31’ 476–620 Central European Highlands spruce forest 19.5 Skuhravá & Skuhravý 1993a
Mallorca (Spain) 39°33’ 02°44’ 1–400 Mediterranean sclerophyll 9.5 Skuhravá & Skuhravý 2004b
Malta, La Valetta 35°54’ 14°30’ 1–240 Mediterranean sclerophll 4.5 Skuhravá et al. 2002
Norway, Harstad 68°48’ 06°30’ 1–3 West European taiga blanket bogs 5 Skuhravá & Skuhravý (in prep.)
Norway, Trondheim 63°25’ 10°25’ 5–560 West European taiga boreal spruce forest 14.0 Skuhravá & Skuhravý (in prep.)
125
Samos (Greece) 37°41’ 27°00’ 1–600 Mediterranean sclerophyll 8.8 Skuhravá & Skuhravý 2006b
Sardinia (Italy) 40°55’ 09°00’ 0-700 Mediterranean sclerophyll 6.5 Skuhravá & Skuhravý 2002
Slovakia, Bratislava 48°08’ 17°07’ 110–2000 Middle European forest, Carpathian forest, Danubian 19.5 Skuhravá 1991
Pannonian thermophilous oak forest
Sweden, Kiruna 67°51’ 20°13’ 330 West European taiga subarctic pine-birch woodland 1.0 Skuhravá (unpubl.)
Sweden, Gävle 60°40’ 17°10’ 1–10 West European taiga subarctic pine-birch woodland 1.0 Skuhravá (unpubl.)
Switzerland, Zurich 47°23’ 08°33’ 208–2044 Central European Highlands montane Scotts pine forest, 16.0 Skuhravá & Skuhravý 1997b
beech forest
United Kingdom, 51°30’ 00°12’ 20–150 British Islands beech and oak forest 14.2 Skuhravá & Skuhravý 2007b
Ripley, Surrey (GB)
Asia: Siberia, Krasnojarsk 56°00’ 92°00’ 350– 1400 Central Asian taiga East Siberian taiga 13.5 Skuhravá & Skuhravý 1993b
in countries of Europe arranged along the latitudinal gradient
over a distance of about 3800 km from the northernmost
investigated area in Norway (Harstad) to the southernmost
investigated area in the island of Malta shows the highest
value between latitudes 45° and 52° North. Species num-
bers in the northernmost localities were low, mainly in tundral
parts of Scandinavia. In contrast, gall midge species numbers
found at the coast in northern Norway were relatively high
owing to the influence of the warm Gulf Stream. Average
species numbers decrease rapidly to the south and in Malta
the average species number per locality was only 5.
On the other hand, the occurrence of gall midge species
along the longitudinal gradient does not produce such
clear results (Fig. 31). The average species numbers of
gall-inducing Cecidomyiidae in countries of Europe along
the longitudinal gradient of 2000 km from the westernmost
investigated area in England to the easternmost area in
Bulgaria at the Black Sea coast in comparison with average
species number in the southern part of Central Siberia seems
to be nearly equal, with two higher values (peaks), viz. in
France, where average species number was 29 owing to the
influence of theAtlantic Ocean, and in Central Europe where
the highest average species number was found in Hungary
situated in the warmer part of the Pannonian lowland.
Climatic factors
Climate and climatic factors have an important influence
on the occurrence and distribution of gall midges in Euro-
pe. Climate includes temperature, humidity, atmospheric
pressure, wind, rainfall and some other elements in a given
region over long periods of time. The climate of a locality is
affected by its latitude, terrain, altitude, ice or snow cover,
as well as nearby water bodies and their currents. Climates
can be classified accordingto the average and typical ranges
of different variables, most commonly temperature and pre-
cipitation which may be shown in graphs, so called clima-
tograms. They represent the sum of two climatic variables,
e.g. temperature and rainfall for a particular geographical
locality and for a specified period, with measurements taken
at regular intervals, usually monthly. In the climatogram
are given the long-term monthly average temperatures (in
a graph on the left side) and the monthly precipitations (in
a graph on the right side) in relation 10° C = 20 mm. When
the precipitation curve falls below the temperature curve, it
is a dry period.
The average species number of gall midges is highest
in Central Europe and decreases towards the south, as was
described in the previous chapters. We compared decreasing
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average gall midge species numbers per locality with climatograms of several parts of Europe and
found that this phenomenon is correlated with climatic conditions and with the temperature and
rainfall (Fig. 32). Central Europe has favourable weather during the year which is characterized
with mild, i.e. not too high temperatures and with a relative sufficient amount of rainfall. The
average gall midge species number in Central Europe is very high, i.e. 26 species in the Czech
Republic and 29 species in Hungary.
The average temperature increses to the south of Europe and, on the other hand, the average
rainfall decreases, which is shown on climatograms for southern Europe where the middle part
of a year with hot and dry weather is figured in black. Hot and dry weather is not too suitable for
the development of gall midges and their galls on host plants. It may be shown that low average
gall midge species numbers occur in the islands of the Mediterranean, viz. only 9.5 species on
average in Mallorca, 9.2 in Crete and even only 4.5 species in Malta.
Long winter periods of cold with low temperatures and short summer periods in northern Europe
do not give suitable conditions for the development of gall midges and their galls on host plants.
On the other hand, a narrow strip (several kilometres only) along the coast in northern Europe
which is under the influence of the Gulf Stream provides suitable conditions for development of
gall midges on host plants and the gall midge species number is there much higher than in inland
parts at the same latitude.
Vertical distribution
The composition of vegetation, including availability of various plant species as potential hosts
for gall-inducing gall midge species, changes with increasing altitude. It is an important value for
zoogeographic analysis. Europe is very varied; the configuration of terrain changes very quickly
Fig. 31. Average species numbers of gall-inducing and plant inhabiting species of the subfamily Cecidomyiinae in coun-
tries of Europe along the longitudinal gradient of 2000 km from the westernmost investigated area in southern England
to the eastermost area in Bulgaria at the Black Sea compared with average species number in the southern part of Central
Siberia. All samples have been taken by the time and area unit collection method. For abbreviations of country names
see Table 1.
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in some parts and large differences in altitudes occur in relatively small areas. We analyzed the
vertical distribution of the gall midge species from localities in several parts of Europe accor-
ding to the altitudinal zones proposed by Ellenberg (1978) that we adapted for different areas. In
Central Europe we usually use eight zones for the area under study, viz. planare zone (from the
sea level–200 m a. s. l.), colline (200–500 m a. s. l.), submountain (500–900 m a. s. l.), mountain
(900–1500 m a. s. l.), sub-Alpine (1500–1700 m a. s. l.), Alpine (1700–2400 m a. s. l.), subnivale
and nivale zones (over 2400 m a. s. l.). Each of these zones is indicated by different abiotic factors,
mainly climatic, and by characteristic composition of vegetation in which there may be present
plant species suitable as hosts for gall-inducing Cecidomyiidae. Altitudinal range of these zones
differ in slopes of mountains or mountain ranges oriented south and north, and with geographic
position.
Elevations of localities at which particular species have been found are an essential basis for
zoogeographic evaluation. For example, in Austria the lowest point is at Neusiedler See at 115 m
a. s. l. and the highest point is the mount Grossglockner at 3797 m a. s. l. We collected galls of
Fig. 32. Europe and its climatic conditions shown in several climatograms. Mild weather conditions in Central Europe are
suitable for development of gall midges. In southern Europe, on islands in the Mediterranean Sea and in northern Africa
dry and hot climates prevail which are not suitable for development of gall midges and for their galls on host plants.
128
gall midges at localities situated in planare zone at 120 m up to the Alpine zone at 2400 to 2500
m. Only a few gall midge species and their associated host plants occur in narrow altitudinal
spans of one zone. Most species occupy larger areas of distribution both in horizontal and vertical
directions and usually are able to occur with their host plants over a relatively large altitudinal
range (Skuhravá & Skuhravý 2009a).
Gall midge species numbers in the planare zone of Europe are usually low and numbers are
usually much higher in colline, submontane and montane zones. Above the boundary of forests,
the so-called timber line (this altitude differs in various parts of Europe in connection with geo-
graphic position), the gall midge species number falls abruptly and only two to four species occur
in the higher zones, i.e. in the sub-Alpine and Alpine zones. The number of gall midge species
therefore decreases with rising altitude.
Of 396 gall midge species forming the fauna of Austria (Skuhravá & Skuhravý 2009a), the
majority occur in colline, submontane and montane zones, only 20 species occur in the sub-Al-
pine zone and 13 species in the Alpine zone. Jaapiella alpina causing galls on Silene acaulis,
Dasineura bistortae on Polygonum viviparum and Hygrodiplosis vaccinii on Vaccinium uligi-
Fig. 33. Vertical distribution of gall midges (Cecidomyiidae) shown as average species numbers in belts of 100 meters in
altitudinal zones of Austria in Central Europe. The average species number falls with rising elevation from the planare
zone up to the subnivale zone where only one gall midge species, Jaapiella alpina causing galls on Silene acaulis (Cary-
ophyllaceae) has been found at altitudes of 2500 m a. s. l. Span of altitudinal zones according to Ellenberg (1978).
129
nosum, found at elevations from 2300–2500 m a. s. l., are true Alpine species associated with
Alpine host plants. In South Tyrol, where intensive investigations were carried out in the Alpine
zone (Skuhravá & Skuhravý, in press) 33 species were found in the Alpine zone. The galls of
Rhopalomyia luetkemuelleri on Artemisia spicata and Jaapiella alpina on Silene acaulis were
found in the subnivale zone at altitudes of 2700 m a. s. l. and are gall midge species found at the
highest altitudes in Europe.
The vertical distribution of gall midges in Europe is shown by average species numbers
recorded at localities in separate successive altitudinal belts of 100 meters (Fig. 33). The basis of
calculations are totals of all species numbers obtained during our own investigations at localities
situated in particular altitudinal zones.
We recognized twenty three types of vertical distribution in the gall midge fauna of Austria
on the basis of their altitudinal span which is given by elevations of the lowest and the highest
situated locality where a particular species was found (Fig. 34). Two fundamental patterns of
vertical distribution were found in each of the lower zones, viz. the occurrence of a species only
inside a particular zone and the occurrence of a species exceeding this zone and reaching higher
zones or running across them to higher altitudinal zones. Few gall midge species and their asso-
ciated host plants occur in narrow altitudinal spans of one zone. These may be named monozonal
species. Most species occupy larger areas of distribution both in horizontal and vertical directions
and usually are able to occur with their host plants in relative large altitudinal range. They may
be named bi-, tri-, or polyzonal species.
Fig. 34. Diagram of twenty-three types of vertical distribution in seven altitudinal zones of Europe recognized in the gall
midge fauna in the course of investigations carried out by present authors at 1821 localities in the years 1955–2009.
130
For example, the gall midges associated with Quercus cerris in Central Europe may be conside-
red to be monozonal and colline species, Macrodiplosis pustularis causing galls on Quercus robur
and Q. petraea is a bizonal species occurring in colline and submontane zones and Oligotrophus
juniperinus inducing galls on Juniperus communis a polyzonal species. It occurs over a large
altitudinal span, including sites in the planare zone up to sites in the Alpine zone. Bisamberg,
190 m a. s. l. in north-eastern Austria was the lowest situated locality where galls were found
and Mount Kanzel, 2348 m a. s. l. in the Alps in northern Italy is the highest point of its known
vertical occurrence (Skuhravá 1987, 1997, Skuhravá & Franz 1989, Skuhravá et al. 2002). O.
juniperinus has a large ecological tolerance and is able to inhabit places that are distant vertically
from each other by more than 2000 meters. O. juniperinus may be considered to be a sub-boreal
and Alpine species.
The occurrence of gall midges in single altitudinal zones may change with geographical position
in Europe. For example, Asphondylia verbasci causing flower gallson various Verbascum species
is in the Czech Republic a colline species occurring from 198 m a. s. l. to 510 m a. s. l., but in
southern Europe, in Bulgaria, it occurs at altitudes of 1400 m a. s. l. in the montane zone.
We prepared detailed analyses of the vertical distribution of gall midge species occurring in
the Czech Republic, Slovakia and Austria and expressed them in graphs (Skuhravá 1991, 1994a,
b, Skuhravá & Skuhravý 2009a).
Frequency
Frequency in ecology is the number of individuals of a species within a given area. In our case,
the frequency is the number of occurrences (given as the number of localities where the species
was found) of a particular gall midge species within a given area. The area under study may be of
varied size from small, including e.g. district, county, region, mount, mountains, island, protected
part of landscape, up to large, e.g. country, Western Europe, Central Europe, zoogeographic or
biogeographic subregion and region, continent. The basis for such analysis is the number of loca-
lities at which a particular species was found, without determining the local abundance of species.
The frequency of animals is usually expressed only by words: very scarce, scarce, moderately
frequent, frequent and very frequent.
For example, if a particular species was found in the area under study at only one locality out
of 60 localities that had been investigated, it is designated as very rare and a species found at 30
localities is designated as very frequent. Species between these two value are denominated by the
terms: scarce, moderately frequent or frequent based only on the experience of the researcher.
On the basis of our rich experiences with the evaluation of frequency of gall midge species
in areas of various size in Europe we developed a unified method for evaluation of frequency of
a particular species in a given area where a particular number of localities was investigated.
If we plotted the occurrence of all species found in the area at localities under study, we received
always the same configuration in the graph, as in Fig. 35. The highest column on the left inclu-
des species each of which was found at only one locality in the course of our investigations, the
number of localities per species reduces very quickly, only a few species occur at more localities
and usually one or two species occur very frequently, each being found at many localities (small
column on the right) (Skuhravá & Skuhravý 2009a). It is possible to divide all species found in
the area under study into six frequency groups by using the first six members of the geometrical
progression with quotient “2” and coefficient “a”:
a.20 + a.21 + a.22 + a.23 + a.24 + a.25 = 63.a (a sum of the progression).
1a + 2a + 4a + 8a + 16a + 32 a = 63 a (simplified)
131
The value of the coefficient may be determinated froma sum of the geometrical progression. Ifwe
investigate an area at 63 localities, the coefficient “a” has the value 1. In other cases it is possible
to count the coefficient “a” from the number of localities that we investigated which is equal to
63a. The extent of each of six frequency group is given by one member of this progression. De-
tails are given in the article of Skuhravá (1994a, b). It is possible to assign verbal denominations
to each of the six group. As an example we give here the calculation of the frequency groups for
Austria in Table 11.
The frequency of gall midge species in Europe is noted for the following shared characters
(Fig. 35). On one side is the group of many very scarcely occurring species that were found only
once in the area under study, some of them were found only at the type locality and have not been
Table 11. Frequency groups of gall midges found in Austria (after Skuhravá & Skuhravý 2009a)
frequency group 1 2 3 4 5 6
members of geometrical progression a.20 a.21 a.22 a.23 a.24 a.25
simplified 1a 2a 4a 8a 16a 32a
number of localities (if a=300) 1–5 6–14 15–33 34–71 72–147 148≤
verbal denomination very scarce medium frequent very most
scarce frequent frequent frequent
Fig. 35. Species of the family Cecidomyiidae found in Austria in the period 1834–2004 arranged in six frequency groups
according to the number of localities at which each species was found. The first column on the left includes 145 gall
midge species which have been found at only one locality. The last column on the right (in the form of a black point)
shows one species, Macrolabis heraclei (Kaltenbach, 1862), causing galls on Heracleum sphondylium (Apiaceae), the
most frequent species in Austria, which was found at 159 localities.
132
found again since that time. They are figured in the graph on the left side. On the opposite side is
the group of a small number of species, sometimes only one or two species, that were found many
times (= at many localities) and are the most frequent species in the area under study. In the graph
they are figured at the right side. Each of four groups between these two extreme groups includes
decreasing numbers of species each of which was found at more and more localities.
We have determined the frequency of gall midges occurring in Europe in some of the countries
where we have carried out investigations, viz. in Slovakia (Skuhravá 1991), Bulgaria (Skuhravá
et al. 1991), the Czech Republic (Skuhravá 1994a, b), Switzerland (1997), Hungary (Skuhravá &
Skuhravý 1999), Denmark (Skuhravá et al. 2006) and Austria (Skuhravá & Skuhravý 2009a). If
there are not such data at our disposal, it is possible to use the number of citations in the literature
to evaluate the frequency of occurrence, as we have done for Portugal and Spain (Skuhravá et al.
2006) and for Poland (Skuhravá et al. 2008), or to combine both methods, as we have done for
France (Skuhravá et al. 2005).
Each part of Europe is characterized by the occurrence of the different groupings of the most
frequent gall midge species. The most frequent gall midge species in the whole of Europe is
Jaapiella veronicae causing galls on leaf buds of Veronica chamaedrys. The galls of this species
were found at 501 localities (of 670 explored) in the Czech Republic (Central Europe) during
investigations in the years 1957–1982 (Fig. 36). In Northern Europe, in Norway, the most fre-
quent species is Iteomyia capreae causing galls on leaves of Salix caprea and related species, in
Denmark Mikiola fagi inducing galls on leaves of Fagus sylvatica and in Poland Lasioptera rubi
causing galls on stems of Rubus idaeus and related species. In France the most frequent species
is Dasineura rosae causing galls on various species of Rosa, in Switzerland Dasineura fraxinea
producing pustule galls on leaves of Fraxinus excelsior, in Austria Macrolabis heraclei causing
galls on leaves of Heracleum sphondylium, in Slovakia Geocrypta galii evoking galls on stems of
Galium mollugo and related species, in Hungary Lasioptera rubi and Dasineura rosae, in Bulgaria
also D. rosae and D. hyperici which causes galls on Hypericum perforatum. All above mentioned
gall midge species belong to faunal elements of the Middle European Forest Province (Fig. 37).
The most frequent gall midge species in the western part of the Mediterranean area – in the
Iberian Peninsula, that is in Spain and Portugal are Phyllodiplosis cocciferae and Dryomyia
lichtensteinii causing galls on leaves and buds of south-European oaks, viz. Quercus coccifera,
Q. ilex and Q. suber, whereas in the eastern part of this area – in Greece – the most frequent spe-
cies is Dasineura turionum changing stems of Asparagus acutifolius into galls. These gall midges
belong to faunal elements of the Mediterranean Sclerophyll Province.
Possibilities of finding additional gall midge species in Europe
Gall-inducing gall midges of Europe are one of the best known gall-causing group of animals in
the world. They can be used therefore as the most suitable group for estimating the number of gall
midges and their galls that may be found in future studies. We try to determine this prognosis using
data from the literature and also data obtained in the course of our investigations in Europe.
We use as the starting point for our prognosis of the increasing species number of the family
Cecidomyiidae in Europe five gall midge species given in Linnaeus (1758) whose 10th edition of
Systema Naturae is the starting point of zoological nomenclature. Bergenstamm & Löw (1876)
summarized knowledge of that time and gave 606 species of the family Cecidomyiidae from all
the world (Table 12). For Europe they gave 492 species. In the subsequent period of 120 years
the number of known gall midges was increased by about five hundred species. Of those, 45 spe-
cies belonged to the subfamily Lestremiinae, 357 to the subfamily Cecidomyiinae and 90 to
undescribed species causing galls. The two last groups form together a group of 447 gall causing
and plant inhabiting species.
133
Kieffer (1898) gave 650 species in his list of the family Cecidomyiidae of Europe and Algeria
where Lestremiinae included 88 species and Cecidomyiinae 562 species, of which 492 species cau-
sed galls or inhabited plants without making galls. From 1876 to 1898 the number of Lestremiinae
increased importantly from 45 to 88 species, i.e. by about 100%, on the other hand the number of
gall-causing species was increased only moderately from 447 to 492, i.e. by about 10%.
Fig. 36. Occurrence of Jaapiella veronicae (Vallot, 1827), causing galls on Veronica chamaedrys L. (Scrophulariaceae),
the most frequent species in Central Europe (black circles). Its galls were found at 510 localities in the Czech Republic.
The density of its occurrence decreases southwards and this species does not occur in the Mediterranean area. White circles
indicate absence of the species. Distribution area of the host plant (black line) after Meusel et al. (1965–1992).
134
Kieffer (1901) summarized knowledge of galls in Europe and gave in his synopsis 1067 spe-
cies of animals belonging to various groups as causers of galls. The family Cecidomyiidae with
364 species was the most species-rich group of gall-inducing animals.
Houard (1908–1909) recorded from Europe and the Mediterranean area 6239 sorts of galls
caused by 1450 species belonging to various groups of animals of which 420 were gall-causing
species of the family Cecidomyiidae (i.e. valid, described species). In addition, he listed about
300 galls, the causers of which were unknown, on various host plants.
Buhr (1964–1965) included 580 valid species (65%) of the family Cecidomyiidae as causers
of galls on various host plants in Central and Northern Europe and about 320 undescribed species
(35%) the causers of which had not been identified because larvae were not known and adults had
not been reared at that time. The relation between described species and undescribed species is
2:1. It is possible to assume that these unknown causers will be found, reared from galls, identified
and described in the future. The gall midge fauna of Europe will thus be enriched in the future by
about 300 species known at the time of Buhr and by another 100 undescribed species associated
with various plant species discovered mainly in the southern parts of Europe from the second
half of 20th century until the present. It is therefore possible to expect about a 50% increase in
the number of valid gall midge species and their galls in the future.
Skuhravá (1986) recorded in the Catalogue of Palaearctic Diptera 1500 species in the family
Cecidomyiidae in Europe of which 170 belong to the subfamily Lestremiinae, 215 to the subfamily
Porricondylinae and 1115 to the subfamily Cecidomyiinae. After 25 years, the number has increased
to 1800 species (Skuhravá 2010, unpublished). The subfamily Lestremiinae includes 280 species,
the subfamily Porricondylinae 310 and the subfamily Cecidomyiinae 1210 species.
In Fig. 38 we show the increasing species numbers of gall midges and increasing number of
galls caused by gall midges during the last 150 years and the lines show the trends of increase.
On the basis of summarized facts we predict that in Europe between the years 2010 and 2050 the
number of gall midges species recorded will increase by about four hundred to 2200 valid species
and the number of galls caused by gall midges by about two hundred to 1400 sorts of galls caused
by gall midges. This is based on the assumption that in the future most of the unidentified causers
of galls will be recognized as good species and described and that new galls and new gall midge
species will be found by future researchers.
Gall midges and host plants
The vegetation covering Europe is relatively species-rich. Tutin et al. (1964–1980) give the
following numbers of plant taxa: 11,557 species, 1541 genera and 203 families. 915 gall midges
species (i.e. valid, described species) forming the subfamily Cecidomyiinae are associated with
280 host plant genera belonging to 72 plant families, i.e. with 18% of plant genera and 35% of plant
families known to occur in Europe. Undescribed gall midge species and species identified to the
Table 12. Number of species of the family Cecidomyiidae in various parts of the world, as given by Bergenstamm &
Löw (1876)
Cecidomyiidae number of species total
Europe N America S America Africa Orient Australia
Lestremiinae 45 1 1 0 0 1 48
Cecidomyiinae 357 42 4 6 4 2 415
unidentified species 90 45 0 7 1 0 143
total 492 88 5 13 5 3 606
135
genus level that are known on the morphology of the gall only are not included in our consideration.
On average one plant genus hosts 3,26 species of gall midges. We analyse relations between gall
midges and their host plant from several points of view, viz. from the phylogenetical system of
plants, abundance of gall midges associated with host plant families and relations between gall
midges and their host plants in different countries of Europe, and the distribution and abundance
of galls on different organs of host plants. See tables 13, 14 and 15.
In Europe only two gall midge species are associated with the Pteridophyta and 27 species
with the Gymnospermae. The majority of gall midges, 886 species, are associated with the Angi-
Fig. 37. The most frequent species of the family Cecidomyiidae in several countries of Europe. See comments in the
text p. 132.
136
Table 13. Gall-inducing and plant inhabiting species of the subfamily Cecidomyiinae associated with plant families and
plant genera in Europe, arranged according to the phylogenetical system of plants according to Tutin et al. (1964–1980)
in Flora Europaea; n1 – number of plant genera; n2 – number of gall midge species
host plants taxa n1 n2 host plants taxa n1 n2
Pteridophyta Dennstaedtiaceae 1 2 Rhamnales Rhamnaceae 2 5
Spermatophyta Vitaceae 1 3
Gymnospermae Malvales Tiliaceae 1 8
Coniferales Hypericales Hypericaceae 1 6
Pinaceae 4 17 Thymelaeales Thymelaeaceae 1 2
Cupressaceae 2 8 Violales Violaceae 1 5
Taxales Taxaceae 1 1 Cistaceae 2 4
Gnetales Ephedraceae 1 1 Tamaricaceae 1 5
Angiospermae Cucurbitales Cucurbitaceae 1 2
Dicotylenodes Myrtales Lythraceae 1 1
Salicales Salicaceae 2 64 Onagraceae 1 2
Fagales Betulaceae 2 14 Umbelliflorae Araliaceae 1 1
Corylaceae 2 10 Cornaceae 1 1
Fagaceae 2 49 Apiaceae 18 28
Urticales Ulmaceae 1 4 Ericales Pyrolaceae 1 1
Moraceae 1 1 Ericaceae 3 15
Cannabaceae 1 1 Primulales Primulaceae 1 1
Urticaceae 1 3 Oleales Oleaceae 4 1
Santalales Loganiaceae 1 1 Gentianales Gentianaceae 1 1
Polygonales Polygonaceae 2 10 Apocyanaceae 1 1
Centrospermae Chenopodiaceae 7 21 Asclepiadaceae 1 2
Caryophyllaceae 9 23 Rubiaceae 2 14
Ranales Ranunculaceae 7 13 Tubiflorae Boraginaceae 4 8
Berberidaceae 1 2 Lamiaceae 20 42
Rhoeadales Papaveraceae 1 1 Solanaceae 1 3
Capparidaceae 1 1 Scrophulariaceae 7 16
Brassicaceae 20 28 Plantaginales Plantaginaceae 1 1
Rosales Saxifragaceae 2 1 Dipsacales Caprifoliaceae 3 11
Grossulariaceae 1 5 Valerianaceae 1 2
Rosaceae 11 49 Dipsaceae 3 4
Fabaceae 28 123 Campanulales Campanulaceae 2 11
Geraniales Geraniaceae 1 2 Asteraceae 25 104
Linaceae 1 1 Monocotyledones
Euphorbiaceae 1 9 Liliiflorae Liliaceae 7 10
Rutales Rutaceae 2 2 Dioscoreaceae 1 1
Polygalaceae 2 1 Juncales Juncaceae 1 1
Sapindales Anacardiaceae 2 3 Graminales Poaceae 31 69
Aceraceae 1 9 Cyperales Cyperaceae 2 27
Celastrales Buxaceae 1 1 Microspermae Orchideaceae 1 1
total 72 plant families, 280 host plant genera, 915 gall midge species
ospermae, of which a smaller part, including 109 species, cause galls or develop in plant organs
of host plants belonging to the Monocotyledones and a larger part, including 777 species, develop
on Dicotyledones.
The Pteridophyta in Europe comprise 25 families of which only one family, Dennstaedtiaceae
(Polypodiaceae), contains only one species – Pteridium aquilinum – that is the host plant of two
gall midge species, Dasineura pteridis and D. pteridicola. Larvae of both species cause simple
galls on leaf margins (bent or rolled parts of leaf margins). These two gall midge species form
only 0,21% of all gall midge species associated with host plants in Europe.
137
The Gymnospermae in Europe comprise five families ofwhich four include host plant species
for 27 gall midge species, i.e.2,95% of all gall midge species associated with host plants in Europe.
The family Pinaceae hosts 17 gall midge species which are associated with four plant genera of
coniferous trees (Abies, Larix, Picea and Pinus). The family Cupressaceae hosts eight gall midge
species associated with two plant genera, viz. Juniperus, hosting seven gall midge species, and
Chamaecyparis, hosting only one gall midge species, which is of North American origin. The
family Taxaceae hosts only one gall midge species, Taxomyia taxi, developing in galls on Taxus
baccata and the family Ephedraceae includes the host plant for only one species, Xerephedromyia
ustjurtensis, causing galls on Ephedra distachya.
About one half of gall midge species developing on host plants of Gymnospermae do not cause
galls at all: two species develop inside seed, five species in cones and five species are associated
with resin. Fifteen gall midge species developing in various plant organs cause galls: two species
induce stem galls, four species cause galls on needles and nine species induce galls in buds. The
galls on Gymnospermae are of various shape. The most primitive seem to be simple swellings
on the bark of Picea abies caused by larvae of Dasineura abietiperda. More complicated are the
galls of Xerephedromyia ustjurtensis caused on stems of Ephedra distachya, which are formed
by swellings of stems with large central chambers containing the larva of the causer. The larvae
of Paradiplosis abietispectinatae induce swellings of needles on Abies alba and the larvae of
Thecodiplosis brachyntera cause swellings at the base of needle pairs on Pinus sylvestris and P.
mugo. Seven species of gall midges cause bud galls on various species of Juniperus, the larvae of
Dasineura kellneri induce galls on buds of Larix decidua and the larvae of Taxomyia taxi change
leaf buds of Taxus baccata into galls.
Fig. 38. Increasing species number of the family Cecidomyiidae during the 19th and 20th centuries and the prognosis
for the future.
138
Of the flowering plants, the Angiospermae are represented by 173 families in Europe, 68 of
which provide host plants for 886 gall midge species, i.e. 96.84% of all gall midge species asso-
ciated with host plants in Europe.
Of the Monocotyledonae, that contain 34 families, only six provide host plants for 109 gall
midge species, i.e. 11.92% of all gall midge species associated with host plants in Europe. Most
of them, totalling 69 species, are associated with various species and genera of Poaceae, 27 gall
midge species with Cyperaceae and 10 gall midge species with Liliaceae. Each of three families,
viz. Dioscoreaceae, Juncaceae and Orchideaceae, hosts only one gall midge species. Most gall
Table 14. Species numbers of gall-inducing and plant-inhabiting gall midges of the subfamily Cecidomyiinae associated
with host plant families in Europe and comparison with occurrence of gall midge species numbers of the same fami-
lies in Kazakhstan (Central Asia). Abbreviations: WE – Western Europe; EE – Eastern Europe; MD Mediterranean;
KZ – Kazakhstan
plant family number of gall midge species plant family number of gall midge species
WE EE MD KZ WE EE MD KZ
Fabaceae 123 60 22 114 Vitaceae 3 0 2 0
Asteraceae 104 33 8 139 Urticaceae 3 1 2 1
Poaceae 69 14 6 16 Solanaceae 3 1 1 3
Salicaceae 64 26 3 18 Anacardiaceae 3 0 1 0
Fagaceae 49 9 18 2 Asclepiadaceae 2 0 0 0
Rosaceae 49 30 16 39 Berberidaceae 2 0 0 2
Lamiaceae 41 15 5 25 Cucurbitaceae 2 0 1 1
Apiaceae 28 7 6 33 Dennstaedtiaceae 2 0 1 0
Brassicaceae 28 8 5 44 Geraniaceae 2 0 1 6
Cyperaceae 27 3 1 1 Onagracceae 2 2 0 1
Caryophyllaceae 23 4 2 15 Rutaceae 2 0 1 0
Chenopodiaceae 21 2 8 90 Thymelaeaceae 2 1 0 0
Pinaceae 17 7 1 2 Valerianaceae 2 0 0 0
Scrophulariaceae 16 9 2 11 Apocyanaceae 1 0 0 0
Ericaceae 15 3 4 0 Araliaceae 1 0 0 0
Oleaceae 15 3 9 0 Buddlejaceae 1 0 0 0
Betulaceae 14 5 0 2 Buxaceae 1 1 0 0
Rubiaceae 14 4 4 14 Cannabaceae 1 0 0 0
Ranunculaceae 13 5 1 14 Capparidaceae 1 0 1 1
Caprifoliaceae 11 3 1 7 Cornaceae 1 0 0 0
Campanulaceae 11 1 0 2 Dioscoreaceae 1 0 0 0
Corylaceae 10 0 2 0 Ephedraceae 1 0 0 9
Polygonaceae 10 1 2 28 Gentianaceae 1 0 0 1
Liliaceae 10 0 2 1 Juncaceae 1 0 0 0
Aceraceae 9 4 3 0 Linaceae 1 0 0 2
Euphorbiaceae 9 3 2 14 Lythraceae 1 0 0 0
Tiliaceae 8 5 0 0 Loganiaceae 1 0 0 0
Cupressaceae 8 2 1 6 Moraceae 1 0 0 0
Boraginaceae 8 1 1 4 Orchideaceae 1 0 0 0
Hypericaceae 6 1 3 0 Papaveraceae 1 0 1 2
Grossulariaceae 5 3 0 3 Plantaginaceae 1 1 0 1
Rhamnaceae 5 1 1 1 Polygalaceae 1 2 0 1
Tamaricaceae 5 0 1 12 Primulaceae 1 1 0 1
Violaceae 5 1 1 1 Pyrolaceae 1 0 0 0
Cistaceae 4 0 0 1 Saxifragaceae 1 0 0 0
Dipsacaceae 4 2 0 0 Taxaceae 1 0 0 0
Ulmaceae 4 2 0 0 total families 73 41 40 54
139
midges totalling 777 species, i.e. 84.92% of all gall midge species associated with host plants in
Europe, are associated with 62 families of the Dicotyledones that contains a total of 139 plant
families.
Gall midges are more diverse on some plant families in which they find more favourable host
plant species and genera for their development. Of the Dicotyledones, the family Fabaceae hosts
the highest number of gall midges – 123 species, followed by Asteraceae with 104 gall midge
species, Salicaceae with 64 species, Fagaceae and Rosaceae, each with 49 species, and Lamiaceae
with 41 species. About two thirds of gall midge species are associated with 12 large plant families
and the remaining third of gall midge species with 61 plant families.
The family Fabaceae hosts 123 gall midge species on plant species belonging to 28 genera,
for example Lathyrus hosts 17 gall midge species, Vicia 14 species, Medicago 11 species, Ge-
nista 10 species, and Trifolium 8 species. The family Asteraceae hosts 104 gall midge species on
25 genera of host plants, for example Artemisia hosts 24 gall midge species, Achillea 7 species,
Hieracium 7 species, Chrysanthemum 6 species, Erigeron 5 species. The family Poaceae hosts 69
gall midge species on 31 genera of host plants, for example Poa 9 gall midge species, Dactylis and
Table 15. Relations of gall-inducing and plant-inhabiting gall midges of the subfamily Cecidomyiinae to host plant spe-
cies in countries of Europe given as the index of mutual gall midge species and plant species occurrence (IGS-PSO); ng
– number of gall midge species; np – number of plant species; index – index of mutual occurrence
country ng np index references to botanical articles
Austria 352 3400 9 Tutin et al. 1964–1980
Belgium 130 1400 11 Tutin et al. 1964–1980
Bulgaria 240 3560 15 Jordanov 1976
Corsica 60 1625 27 Rikli 1946
Crete 38 2200 58 Rikli 1946, Sfikas 1987
Cyprus 32 1800 56 Sinclair 1991
Czech Republic 564 2200 4 Kubát 2002
Faroe Islands 5 400 80 Fosaa 2000
France 581 4500 8 Tutin et al. 1964–1980, Rikli 1946
Germany 653 2800 4 Jäger & Werner 2007
Greece 211 6700 32 Rikli 1946
Hungary 332 4200 13 Soó 1973
Italy 315 5600 18 Pignatti 1982
Italy (South Tyrol) 312 2361 7 Wilhalm & Hilpold 2006
Latvia 264 1385 5 Flora of Latvia 1953–1959
Mallorca 33 1250 37 Tutin et al. 1964–1980
Malta 36 1250 35 Haslam et al. 1977
Netherlands 305 1500 5 Tutin et al. 1964–1980
Poland 397 2500 6 Szafer et al. 1986, Mirek et al. 2002
Portugal 122 2735 22 Rikli 1946, Castroviejo 1986–2005
Romania 304 3600 12 Hayek 1927–1933, Savulescu 1952
Russia (European) 400 6500 16 Tutin et al. 1964–1980
Sardinia 44 2000 45 Tutin et al. 1964–1980
Sicily 89 2200 25 Tutin et al. 1964–1980
Slovakia 355 3352 10 Baláž et al. 2001
Slovenia 219 3200 15 Martinčič & Sušnik 1999
Spain 212 6500 30 Castroviejo 1986–2005
Sweden 266 2000 8 Karlsson 1998
Switzerland 228 3500 15 Lauber & Wagner 2001
Ukraine 166 3700 22 Bordzilowskij 1938
United Kingdom 526 2200 4 Fitter & Peat 1994
140
Festuca each 5 species, Alopecurus, Bromus, Calamagrostis and Phragmites each 4 gall midge
species. In contrast, the family Salicaceae hosts 64 gall midge species which are associated with
only two plant genera: Populus with 14 gall midge species and Salix with 50 gall midge species.
Also in the family Fagaceae only two plant genera are associated with gall midges: Fagus hosts
6 gall midge species and Quercus 43 gall midge species.
Most gall midges that are associated with Angiospermae induce galls on various plant organs
and only a few develop on or in organs of host plants without inducing gall development. Larvae
of plant-inhabiting, i.e. not gall-inducing gall midges, live under the leaf sheaths of grasses, inside
plant stems, under the bark of living, injured or dying trees, in resin masses, in inflorescences, in
or on seeds and in cones. About one half of gall-inducing gall midge species cause galls on flowers
and leaf buds, others induce galls on leaves and only a small part develop inside fruits.
In Western Europe 915 gall midge species are associated with 72 plant families and 12.5 is the
average number of gall midge species per plant family; in Eastern Europe 287 gall midge species
are associated with 41 plant families and 7 is the average number of gall midge species per plant
family; in the Mediterranean 153 gall midge species are associated with 40 plant families and
3.8 is the average number of gall midge species per plant family. As it is shown, the western part of
Europe is more species rich than the eastern part and the Mediterranean is notably species poorer.
Surprisingly, the gall midge fauna of Kazakhstan in Central Asia is more species rich including
714 gall midge species that are associated with 52 families (according to Fedotova 2000), and
13.5 is the average gall midge species number per family.
In Western Europe 115 gall midge species are associated with Fabaceae and 100 species with
Asteraceae. Host plants of the family Fabaceae, with 60 gall midge species, are also in first place
in Eastern Europe and in the Mediterranean. On the other hand, in Kazakhstan the highest species
number of gall-inducing gall midges 139 species is associated with the family Asteraceae
the species of which form the main plant associations in desert and semidesert areas of Central
Asia. In Western Europe a large amount – 69 species – are associated with Poaceae, 64 species
with Salicaceae and 49 species with Fagaceae. Gall midge species associated with plant families
including trees and shrubs (Salicaceae, Fagaceae, Pinaceae, Oleaceae, Betulaceae, Corylaceae,
Aceraceae, Tiliaceae, Cupressaceae, Rhamnaceae, Tamaricaceae and Ulmaceae) and including
about 200 gall-inducing species markedly predominate gall midge species associated with her-
baceous plants.
The gall midge fauna of Eastern Europe including 287 gall-inducing species that are associated
with 41 plant families is similar to that occurring in Western Europe but the species number as-
sociated with trees and plants is much lower. For example, only 26 gall midge species are known
to occur on Salicaceae, in contrast to 64 species occurring in Western Europe and 9 species on
Fagaceae in contrast to 49 species in Western Europe.
The gall midge fauna occurring in nine islands situated in the Mediterranean Sea and including
153 gall midge species that are associated with 40 plant families is relatively poor.
Gall midge species cause galls mainly on herbaceous plants of the family Fabaceae and on trees
and shrubs of the family Fagaceae in second place. Islands in the Mediterranea area are densely
covered with broad-leaved forests with dominant tree species of the genus Quercus including
many species that are host plants of many gall midge species.
Kazakhstan is a large country situated in Central Asia and with only a small part in Eastern
Europe. It occupies an area of 2,727,300 kwhich is greater than Western Europe. It includes very
diverse types of landscape: lowlands with steppes, taigas, rock-canyons, hills, deltas, mountains,
snow-capped mountains and deserts. The flora of Kazakhstan is rich and includes about 6000 plant
species in 1118 genera and 161 families (Ryabushkina et al. 2008). Gall midge fauna occurring in
Kazakhstan is also rich: 714 gall-inducing species are associated with 54 plant families, i.e. with
141
33% of all plant families known in Kazakhstan (Fedotova 2000). Asteraceae with 139 gall-inducing
species is the richest family, followed by Fabaceae hosting 114 species, Chenopodiaceae with 90
species, Brassicaceae with 44 species and Rosaceae with 39 gall midge species. In Kazakhstan,
compared with Western and Eastern Europe, the majority of gall-inducing gall midge species are
associated with herbaceous plants and only a few species cause galls on trees and shrubs.
If we compare the species richness of gall midges in the four mentioned areas using the average
species number per one host plant family, Western Europe with 12.5 gall midge species associa-
Fig. 39. Relations of gall-inducing and plant-inhabiting gall midges of the subfamily Cecidomyiinae to host plant species
in countries of Europe given by the index of mutual occurrence.
142
ted with one plant family is in first place, followed by Eastern Europe with 7 gall midge species
associated with one plant family and the Mediterranean with 3.8 gall midge species associated
with one plant family in last place in Europe. Of interest is the comparison of data from Europe
with data obtained in Kazakhstan situated in Central Asia where it has been found that an average
13.5 gall midge species are associated with one plant family.
Mutual occurrence of gall midges and host plants
As we have shown in previous sections, gall midges are not equally distributed in countries
of Europe. We try to analyse the relations between the species numbers of gall midges and the
numbers of plant species in particular countries and islands of Europe (Table 15). It is necessary
to mention that the numbers of species of flowering plants occurring in particular country given
by various authors sometimes differ importantly. For some countries we were not able to obtain
recent data of species numbers of flowering plants.
For the comparison of relations between gall midges and host plants we introduce here the
formula – the index of mutual gall midge species and plant species occurrence (IGS-PSO),
as follows:
IGS-PSO= NPS/NGMS
where NPS is the number of plant species in a particular country and NGMS is the number of gall
midge species occurring in the same part. This index indicates the degree of mutual occurrence
of gall midges on host plants in particular parts of Europe (Table 15, Fig. 39).
For example. If 5000 plant species have been recorded in a particular country and the fauna
of gall midges of that country includes 500 gall midge species, the index is IGS-PSO=5000/500
and the result after calculating is 10. This number indicates a high value of mutual occurrence of
gall midge species and host plants in that country. It means that we may find in such a country
an average of one gall midge species on every tenth plant species. If in such a country the gall
midge fauna includes only 100 gall midge species, the index IGS-PSO=5000/100 and the result
after calculating is 50. In such a case we should find one gall midge species on every 50th plant
species. Such a result indicates that the fauna of gall midges associated with plant species in
a particular country is poor.
Table 16. Distribution of galls of eleven major genera of gall-inducing Cecidomyiinae on different organs of host plants
in Europe
gall midges n species organs of host plants inquiline biology
genus stem bud leaf flower fruit unknown
Dasineura 230 20 62 62 56 19 17
Contarinia 135 6 18 17 80 9 3
Asphondylia 50 0 13 1 20 19 0
Rabdophaga 40 20 16 4 0 1 1
Rhopalomyia 38 4 18 7 5 0 4
Jaapiella 35 0 10 8 12 1 4
Macrolabis 35 0 9 5 5 0 15
Mayetiola 28 27 0 0 0 0 0 1
Lasioptera 27 16 0 2 0 0 5 4
Planetella 27 8 0 6 0 0 0 13
Resseliella 23 13 1 0 0 4 2 3
total 668 114 147 112 178 53 51 21
143
It is necessary to note that the value of the index is greatly influenced by the intensity of inves-
tigation of the gall midge faunas of the various countries and islands as well as by the diversity
of the flora. For example, the UK low figure results from the combination of a depauperate post-
-glacial flora and long-term study of galls (K. M. Harris, pers. comm.).
Countries in Europe with an index value from 1 to 4 are noted for the highest mutual occurrence
of gall midges and host plants. The United Kingdom, Germany and the Czech Republic having
an index number of 4 are the countries with the highest mutual occurrence of gall midges and
host plants in Europe. Countries characterized by an index value from 5 to 10 are noted for high
mutual occurrence, viz. Latvia, the Netherlands, Poland, South Tyrol, France, Sweden, Austria
and Slovakia. Eight countries, viz. Belgium, Romania, Hungary, Bulgaria, Slovenia, Switzerland,
European part of Russia and Italy having been characterized by the index numbers from 11 to 20
may be evaluated as countries with medium mutual occurrence of gall midges and host plants.
Five countries, viz. Spain and Portugal, Corsica, Sicily and Ukraine, characterized by the index
numbers from 21 to 30, are countries of weak mutual occurrence of gall midges and host plants.
Greece and five islands in the Mediterrranean Sea (Mallorca, Sardinia, Crete, Malta and Cyprus)
with index numbers from 31 to 60 are countries with poor mutual occurrence of gall midges and
host plants. The Faroe Islands situated in the Atlantic Ocean in northern Europe have a very poor
mutual occurrence of gall midges and host plants characterized with the index number 80.
Although Greece is in Europe the country with the richest flora, including 6700 species of
flowering plants, the gall midge fauna of Greece, including 211 species, may be classed as poor.
Table 17. Species numbers of gall-inducing Cecidomyiinae associated with main broad-leaved and coniferous trees in
Europe. Abbreviations of countries: A – Austria, CH – Switzerland, CZ – Czech Republic, D – Denmark, F – France,
P – Poland (data from Skuhravá & Skuhravý 1997a, b, 2009a, Skuhravá et al. 2002, 2005, 2006, 2007, 2009, Skuhravý
& Skuhravá 1998)
gall midge species number
Europe F A CH CZ P D Sicily Malta Crete
broad-leaved trees
Fagus sylvatica 4 4 4 3 4 4 4 2 0 0
Quercus robur 15 14 8 3 6 7 7 0 0 0
Acer pseudoplatanus 4 4 4 4 4 4 3 1 0 0
Fraxinus excelsior 5 4 4 3 4 4 3 0 0 0
Tilia platyphyllos 8 5 6 5 5 5 5 0 0 0
Betula pubescens 10 6 4 2 5 4 5 0 0 0
Carpinus betulus 6 5 4 4 5 4 3 0 0 0
Populus tremula 13 11 9 8 9 10 7 0 0 0
Salix caprea 7 13 6 2 7 9 9 0 0 0
Olea europaea 4 2 0 0 0 0 0 4 1 2
Quercus cerris 13 2 9 0 8 1 0 1 0 0
Quercus ilex 5 5 0 0 0 0 0 4 0 0
total 94 75 58 34 57 52 46 12 1 2
coniferous trees
Picea abies 5 4 4 3 4 5 5 0 0 0
Pinus sylvestris 5 3 4 3 3 3 4 0 0 0
Abies alba 3 2 2 0 2 2 3 0 0 0
Larix decidua 3 2 2 1 2 3 2 0 0 0
Juniperus communis 7 4 2 2 3 4 3 0 0 0
Taxus baccata 1 1 1 1 1 1 1 0 0 0
total 23 16 15 10 15 18 18 0 0 0
144
We obtain similar relations between the rich flora of Spain including 6500 species of flowering
plants and 212 gall midge species found. Similar relations between rich floras and poorgall midge
faunas were found in islands in the Mediterranean Sea, viz. in Mallorca, Corsica, Sardinie, Sicily,
Malta, Corfu, Crete and Cyprus.
The analysis of the relationship between gall-inducing and plant-inhabiting gall midges of the
subfamily Cecidomyiinae and potential host plant species in the countries of Europe produced
a surprising result: although number of species of flowering plants increases from north to south,
the species number of gall midges decreases.
Distribution of galls on host plants
Galls of gall-inducing species of the subfamily Cecidomyiinae are not equally distributed on
organs of their host plants. We analysed eleven genera of gall-inducing Cecidomyiinae occurring
in Europe on the basis of which organ of host plant is used for development of their larvae (Table
16). Of 668 species belonging to these eleven genera, 90% induce galls on various plant organs,
7% are inquilines in galls of other gall midges or insects and the biology of 3% is completely
unknown. Species of the genus Dasineura cause galls mainly on buds and leaves, of the genus
Contarinia on flowers, of Asphondylia on flowers and fruits, of Rabdophaga on stem and buds,
of Rhopalomyia on buds, of Jaapiella on buds and flowers, species of the genus Macrolabis are
mainly inquilines in galls of other gall midges and species of Mayetiola, Lasioptera, Planetella
and Resseliella develop in galls mainly on stems. Some species that have two or more generations
per year may cause galls on two or more different organs of their host plant and therefore the sum
of inhabited plant organs in the table does not equal the number of gall midge species.
Abundance of gall midge species on host plant species
We use the term abundance here for the number of species associated with one host plant species.
Different numbers of species or genera of gall-inducing gall midges may develop on one host plant
species. The occurrence of gall midges (Cecidomyiidae) on host plants, mainly on trees, is not so
abundant as that of gall wasps (Cynipidae, Hymenoptera). For example, about 130 different gall-
-inducing species of gall wasps, belonging to several genera, are associated with Quercus robur
and Quercus petraea (Fagaceae) in Europe but only fifteen gall-inducing species of gall midges,
also belonging to several genera (Skuhravá et al. 1998).
If we analyse the gall midge faunas of European countries from the point of view of association
with host plants, we find that herbaceous plants are more frequently host plants than trees and
shrubs. Although trees and shrubs host fewer gall midge species than herbaceous plants, their
galls on leaves are usually more conspicuous and, therefore, much better known than small and
inconspicuous galls on herbaceous plants that are hidden among grasses near the soil.
For example: the gall midge fauna of Poland includes 397 species of the subfamily Cecido-
myiinae that are associated with 257 species of host plants belonging to 48 plant families of which
197 species (76%) are herbaceous plants and 60 species (24%) trees and shrubs (Skuhravá et al.
2008). Similar relationships between number of herbaceous plants and trees/ shrubs as host plants
were found in the gall midge fauna of Austria (Skuhravá & Skuhravý 2009a) and of Denmark
(Skuhravá et al. 2006). In Europe about 70% of gall-inducing species of the subfamily Cecido-
myiinae are associated with herbaceous plants and only 30% with trees and shrubs.
Many tree species are hosts of one, two, three or more gall midge species. Some gall midge
species are monophagous and are associated with only one host plant species, some are oligo-
phagous having been associated with several species of one host plant genus and only a few gall
midge species are polyphagous and are associated with species of several genera belonging to
145
one or more plant families. Gall midge species associated with twelve main broad-leaved tree
species and six coniferous trees in Europe are given in the Table 17.
Altogether one hundred and seventeen gall-inducing and plant inhabiting species are associated
with eighteen main tree species in Europe. Ninety four gall midge species are associated with
twelve main broad-leaved host tree species and twenty three gall midge species with six coni-
ferous trees. These trees are not distributed equally in Europe and, naturally, gall midge species
coincide with their host plants in distribution. Quercus robur is the host tree species with the
highest species number of Cecidomyiidae (15 species), followed by Populus tremula and Quercus
cerris, each with thirteen gall midge species, then Betula pendula with ten gall midge species and
Tilia platyphyllos with ten gall midge species. Olea europaea is the south-European plant species
and the boundary of its distribution area are considered to be the boundary of the Mediterranean
subregion. Gall midge species associated with broad-leaved trees occurring in Sicily, Malta and
Crete, parts of the Mediterranean subregion, form a characteristic species composition which
differs substantially from the gall midge species composition in other parts of Europe.
France, situated in the most western part of Europe bordering the Atlantic Ocean has the richest
gall midge species composition including 75 species that are associated with broad-leaves trees
and also the highest species numbers of gall midges associated with one species of host plant. It is
composed not only of gall midge species abundantly distributed in Central Europe but also includes
nine gall midge species associated with Quercus cerris, Q. ilex and Olea europaea originating
from the Mediterranean area and distributed only in the southernmost part of France. Some of
these gall midges reach to the southern parts of Austria and of the Czech Republic.
In Poland and Germany, situated in the northern part of continental Europe, there was found
the highest gall midge species number associated with coniferous trees. This is in harmony with
character of vegetation in this part of Europe. No gall midge species associated with coniferous
tree was found in Sicily, Malta and Crete that are situated in the Mediterranean area.
Coevolution of the family Cecidomyiidae with plants
Coevolution is definedby Lincoln etal. (1982) as the independentevolution of two ormore species
having an obvious ecological relationship, usually restricted to cases in which the interactions
are beneficial to both species; it is also used for the evolutionary interactions between species
with some degree of independence, such as parasites and their hosts. Such relationships may be
observed between the gall midges and their host plants, host animals or other host organisms in
the course of their evolution.
No members of the family Cecidomyiidae are known to be associated with the most primitive
groups of organisms, i.e. with Prokaryota and Algae, and no gall midges have been found to be
directly associated with lichens (Lichenes) (Table 18, Fig. 40). It seems that at least two main
developmental lines of gall midges appeared during their evolution. In the past, members of the
family Cecidomyiidae were probably involved in interactions with three groups of fungi, i.e. with
Ascomycetes, Basidiomycetes and Deuteromycetes. This is supported by the fact that in the recent
time we have evidence that the larvae of gall midges develop in association with various groups
of fungi (Nijveldt 1969, Skuhravá et al. 1984, Yakovlev 1994, Ševčík 2006).
The current associations may result from more than one coevolutionary event. We know that
the ability of organisms to induce galls has arisen on many separate occasions so the same may
be true within cecidomyiid lineages. Coevolution of gall-inducing and plant inhabiting species of
the family Cecidomyiidae with two groups of vascular plants, Pteridophyta and Spermatophyta,
is shown on Fig. 40. Plant groups marked by red frames indicate host plant species suitable for
development of gall midges.
146
The ferns (Pteridophyta) first appeared in the fossil record in the early-Carboniferous period.
By the Triassic, the first evidence of ferns related to several modern families appeared. The“great
fern radiation” occurred in the late-Cretaceous, when many modern families of ferns first appeared.
There is no fossil evidence of galls of gall midges on ferns and only two extant gall midge species
are known to occur on ferns in Europe, viz Dasineura pteridis and D. pteridicola, both causing
galls on Pteridium aquilinum of the family Dennstaedtiaceae.
The seed plants (Spermatophyta, Gymnospermae) originated in the late Carboniferous Period.
Early characteristics of seed plants were evident in fossil Progymnospermes of the late Devonian
period around 380 million years ago. Conifers are by far the most abundant gymnosperms with
around 600 plant species. Only one fossil record supports the coevolution of gall midges with
conifers – Sequoiomyia kraeuseli found in fossil cones of Sequoia langsdorfii of the family Ta-
xodiaceae. A relatively low species number of twenty six gall midge species currently occurring
in Europe indicates a low degree of coevolution.
Cycads are the next most abundant group with about 130 plant species and without fossil evi-
dence of coevolution with gall midges. Gnetales included approximately 75–80 species. There
is no fossil evidence about the galls of gall midges on Gnetales. Only one recent gall midge spe-
cies is known – Xerephedromyia ustjurtensis inducing galls on Ephedra distachya of the family
Ephedraceae in Europe.
Fig. 40. Coevolution of gall-inducing and plant inhabiting species of the family Cecidomyiidae with two groups of vascular
plants, Pteridophyta and Spermatophyta, according to the phylogenetic system proposed by Kenrick & Crane (1997) and
Smith et al. (2006). Plant groups marked by red frames indicate host plant species of gall midges.
147
The flowering plants (Magnoliophyta, Angiospermae) are the most abundant group of plants,
including about 260,000 recent and many fossil species. Most gall midges known to occur in
Europe, including 870 recent species, are associated with this group of plants. Fossil galls of ten
gall midge species provide evidence of their coevolution with flowering plants in the Miocene
and Pliocene of the Tertiary in various parts of Europe.
Adults of eighty-nine fossil species of 54 genera of the family Cecidomyiidae are known from
various parts of the world (Evenhuis 1994, Skuhravá 2006). Fossil gall midge adults were found
mainly in amber and copal and are dated from the Upper Jurassic, Lower Cretaceous, Upper
Cretaceous, Eocene, Oligocene, Miocene, Pliocene and Holocene. Fossil gall midge adults were
found scattered in all biogeographic regions except the Australasian and Oceanian regions. The
oldest fossil gall midge species, Catotricha mesozoica Kovalev, 1990, found in Siberia from the
Upper Jurassic and Lower Cretaceous, provides evidence that members of the Lestremiinae and
Porricondylinae probably originated and developed in the Mesozoic (Kovalev 1990).
In Europe, fossil gall midge adults were found mainly in amber of the Baltic Region. They
belong mainly to the subfamilies Porricondylinae and Lestremiinae and only a very few species
are Cecidomyiinae. Single species, sometimes identified to the genus level only, were found
in the UK, Denmark, Germany, France, Austria and Italy. Fossil adults of several gall midge
species were discovered in the earliest Eocene amber in northern France (Nel & Prokop 2006)
and in later Eocene amber in western Ukraine (Fedotova & Perkovsky 2004, 2005, Perkovsky
& Fedotova 2004).
There are only a few data about fossil galls induced by gall midges on organs of fossil host
plants in the world (Larew 1992). In Europe the galls of ten gall-causing species were found,
mainly in the form of the leaf impressions of host plant trees from the Tertiary Upper Miocene
and Pliocene (Trotter 1903, Rübsaamen 1929). Möhn (1960) discovered the fossil gall midge
species Sequoiomyia kraeuseli in the cone seeds of the fossil plant Sequoia langsdorfii (Taxodi-
aceae) in Rheinland (Germany) from the Miocene. Straus (1977) mentioned among fossil galls
Table 18. Recent species numbers of the family Cecidomyiidae associated with the main groups and subgroups of or-
ganisms in Europe. Groups of vascular plants are given according to the phylogenetical system proposed by Kenrick &
Crane (1997) and Smith et al. (2006)
phylogenetical group or subgroup of organisms and plants recent species number of gall midges
Prokaryota Cyanophyta 0
Bacteriophyta 0
Algae 0
Mycophyta (fungi) Ascomycetes 7
Basidiomycetes 70
Deuteromycetes 0
Lichenes 0
Bryophyta (mosses) 0
Vascular plants Pteridophyta (ferns) Pteridopsida (true ferns) 2
(897 gall midge species) Spermatophyta Cycadophyta 0
(Gymnospermae) Pinophyta (conifers) 26
(seed plants) Ginkgophyta 0
Gnetophyta 1
Magnoliophyta (Angiospermae)
(flowering plants) 870
148
found at Willershausen in Harz (Germany) in the Pliocene also six fossil galls that were probably
caused by species of the family Cecidomyiidae. Villalta (1957) found in Spain traces of galls
which he identified as Mikiola pontiensis. It was a misidentification. On the basis of their form,
these galls were caused by another gall midge species – Phegomyia fagicola (Kieffer, 1913), an
extant species (Skuhravá 2006). Information about fossil galls caused by gall midge species is
summarised in Table 19.
Fossil galls of ten gall midge species were found on nine genera of host plants belonging to
eight plant families. Most gall midges induced galls on leaves and only one species inhabited
cones. Fagaceae are the plant family hosting the highest number of gall midges – four species,
and each of the other families hosts only one gall midge species.
It is necessary to note that three gall midge species given in Table 19 were incorrectly identi-
fied in the past. Identification of the species causing galls on leaves of Fagus castaneifolia was
corrected by Skuhravá (2006). The galls on leaves of Betula are caused by another species, not
by Contarinia carpini which is specifically associated with Carpinus. Also the galls on leaves
of Quercus given as Phegomyia fagicola were incorrectly identified. P. fagicola is specifically
restricted to Fagus and could not cause galls on leaves of Quercus.
During evolution, the gall-inducing and plant inhabiting gall midges of the subfamily Ceci-
domyiinae probably started to develop at the end of the Mesozoic when they entered into inte-
ractions with developing groups of plants, started to inhabit suitable parts of plants, their organs
Table 19. Fossil galls induced by gall midges of the subfamily Cecidomyiinae on host plants found in Europe
gall midge species host plant host family host organ locality age reference
Sequoiomyia Sequoia langsdorfii Taxodiaceae cones Germany: Duren Miocene? Möhn 1960
kraeuseli
Asphondylia Sarothamnus Fabaceae leaf Europe, not precised tertiary Rübsaamen
sarothamni 1929
Cecidomyia sp. Populus Salicaceae leaf Switzerland: Oeningen tertiary Trotter 1903
Contarinia Betula Betulaceae leaf Germany: Willershausen pliocene Straus 1977
carpini (misidentification)
Dasineura Fraxinus Oleaceae leaf Germany: Willershausen pliocene Straus 1977
fraxini
Dasineura Carpinus Corylaceae leaf Germany: Willershausen pliocene Straus 1977
ruebsaameni?
Didymomyia Tilia Tiliaceae leaf Germany: Willershausen pliocene Straus 1977
tiliacea
Mikiola fagi Fagus pliocenica Fagaceae leaf France: pliocene Marty 1894
Pas-de-la-Mougudo
Mikiola fagi Fagus Fagaceae leaf Europe, not precised tertiary Rübsaamen
1929
Phegomyia Fagus Fagaceae leaf Spain: Cerdãna miocene Villalta
fagicola castaneaefolia 1957,
(misidentified) Skuhravá
as Mikiola? pontiensis 2006
Phegomyia Quercus Fagaceae leaf Germany: Willershausen pliocene Straus 1977
fagicola
(misidentification)
149
and tissues inducing there changes that initiated the formation of galls. The main development of
gall-inducing and plant inhabiting gall midges came in the Pliocene and Miocene of the Tertiary,
together and in parallel with the development of flowering plants, as is supported by the evidence
of several fossil galls of gall midges.
Factors affecting gall midge species richness
From our observations and literature research we conclude that gall midge species richness is
influenced mainly by abiotic factors, i.e. by geographic and altitudinal position of the area under
study that are associated with changing climatic variables including sunshine, temperature and
rainfall; by biotic factors, i.e. mainly by the type of vegetation cover and composition of natural
vegetation; and by anthropic factors, involving various human activities. The present species
richness and distribution of gall midge species in Europe are results of all these influences which
are brieflycommented on below.In most cases detailedinformation is provided in earliersections
of this article.
Geographic position. In Europe the most suitable area for gall midges is the temperate zone
situated between latitudes 45° and 52° North, which is covered with broadleaved, coniferous and
mixed forests. Gall midge species number changes with geographical position and decreases both
northwards and southwards. On the other hand, species numbers of gall midges are relatively
stable along the west-east axis. The exceptionally low gall midge species number in the Faroe
Islands, situated in the Atlantic Ocean far off the European continent, is the result of geographical
isolation.
Altitude. Generally speaking, the number of gall midge species decreases with rising altitude.
Species numbers in the planare zone of Europe are usually low and are much higher in colline,
submontane and montane zones. Above the timber line, usually at an altitude of about 1500 m
in Europe (this altitude differs in various parts of Europe with geographic position) the species
number falls abruptly and only a few species occur in the sub-Alpine and Alpine zones.
Climatic factors. Gall midge species number is relative high in Central, Western and Eastern
Europe and falls to the south. This corresponds with changing climatic factors that are shown in
climatograms: the temperature increases to the south and, on the other hand, the rainfall decreases
and the hot and dry weather in southern Europe may be unsuitable for the development of gall
midges and their galls on host plants.
Composition of vegetation. Richness of plant species, providing plenty of potential hosts for
gall midges, is the most important prerequisite of richness of gall midges in the area. When we
compared the number of plant species in various parts of Europe with the number of gall midge
species, we discovered a very surprising fact that the number of gall midge species decreases to
the south of Europe although the number of plant species increases.
Association with host plant species. Most gall-inducing gall midges are specificallyrestricted to
their host plants and usually mirror the distribution of their host plants in their native environments,
but in a few cases their distribution may be extended into new areas when their host plants become
established in distant areas, such as Siberia, the Far East or even North America.
Anthropic factors. People have changed landscapes in Europe for a long time. Mediterranean
areas have been exploited in ancient times by clearing, burning and grazing and natural forests
have been replaced by olive trees, carob, wine grapes and citrus trees. Also landscapes in other
parts of Europe changed under influence of man which gradually decreased the number of gall
150
midge species. Some species that were abundant in the past disappeared as a result of the degra-
dation and destruction of biotopes, the use of chemical agents in plant protection against pests and
intensive fertilization of fields, cuttingand burning of grasson headlands andfallows, destruction
of small forest areas, use of land for new building activities, park and orchard arrangements with
regular cutting of grass, cutting of grass on slopes, formerly left without human interventions,
cutting of reeds and adjustment of littoral growths, amelioration of wetlands and wet meadows.
In the course of all these activities, the natural growth and multiplication of host plants of gall
midges is restricted and thus, the populations of plants and animals that are dependent on them
(including Cecidomyiidae) are progressively reduced (Skuhravá 2005).
Intensity of investigations. Results of gall midge species numbers in the area under study are
affected also by the number of investigations and by selection of suitable sites for collection of
gall midges. More investigations and more samples usually result in increased species numbers,
new records and also discovery of new species. It is necessary also to emphasize the importance
of the researchers, their ability, experience, knowledge and enthusiasm that make it possible
to discover gradually additional gall midge species and hidden factors influencing gall midge
species richness.
A c k n o w l e d g e m e n t s
We would like to express our thanks to Keith M. Harris (Ripley, Woking, Surrey, England) for valuable comments on the
manuscript and for improvements of the English text. We thank Jan Zárybnický, Agency for Nature Conservation and
Landscape Protection of the Czech Republic, Prague, for all advice and for preparing maps according to the map basis of
© ESRI® & NASA, 2007. We thank Torbjörn Tyler, Botanical Museum, Lund, Sweden, for data on recent and past plant
species numbers of Sweden. We are grateful to our daughter, Ivana Vaněčková, and our granddaughter, Pavla Kosová,
for their help in preparing computer version of graphs.
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... The nomenclature of gall midge species is based on Gagné & Jaschhof (2017), the nomenclature of host plant species on Tutin et al. (1964Tutin et al. ( -1980 and The Plant List (Anonymous 2013). The economic importance of gall midge species was assessed based on information in Barnes (1946Barnes ( -1956, Nijveldt (1969), Darvas et al. (2000) and Skuhravá & Roques (2000), zoogeography on Skuhravá & Skuhravý (2010). ...
... Distribution is based on data of occurrence of gall midges in the Palaearctic region (Skuhravá 1986), in the world (Gagné & Jaschhof 2017), on analysis of areas of distribution (Skuhravá 1980, 1987, Skuhravá et al. 1984) and on results of investigations of M. Skuhravá and V. Skuhravý carried out in the years 1955-2013 at 1898 localities situated in twenty three countries of Europe and twelve islands in the Mediterranean Sea which were published in series of articles cited in Skuhravá & Skuhravý (2010); further on data given in Jaschhof (1998), Fedotova (2000, Mirumian (2011), Skuhravá (2016, Skuhravá & Skuhravý (2016a, b), and Skuhravá et al. (2013Skuhravá et al. ( , 2014aSkuhravá et al. ( , b, c, 2017a. ...
... Near alger (on Hippomarathrum pterochlaenum Boiss.) (Bequaert 1914, Dorchin & Freidberg 2011, Skuhravá & Skuhravý 2010. Distribution. ...
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The known fauna of gall midges in Algeria is composed of 109 valid species belonging to 43 genera, and four undescribed species. It is the richest fauna of five countries spread along the Mediterranean Sea in North Africa. Twenty five species of gall midges were decribed on the basis of material collected in Algeria and have there their type localities. The two most abundant species of gall midges in Algeria are Asphondylia punica Marchal, 1897, causing galls on Atriplex halimus, and Rhopalomyia navasi Tavares, 1904, inducing galls on Artemisia herba-alba. Galls of R. navasi were recorded at two localities in northwestern Algeria recently, in the year 2015. the most species rich genus is Dasineura Rondani, 1840, with twenty five species, followed by Asphondylia Loew, 1850 (ten species), Contarinia Rondani, 1860 (eight species), and Stefaniola Kieffer, 1913 (seven species). On the basis of larval feeding habits most species are phytophagous, ten species are mycophagous and Aphidoletes aphidimyza (Rondani, 1847) and Arthrocnodax clematitis Marchal, 1897 are zoophagous. Phytophagous species are associated with 83 host plant species belonging to 65 genera of 29 plant families. Chenopodiceae is the plant family hosting the highest number of gall midges-sixteen species of gall midges. Three quarter of host plant species are herbaceous plants and one quarter trees or shrubs. Usually only one species of gall midge is associated with one host plant species. Four host plants-Atriplex halimus, Fraxinus excelsior, Phillyrea latifolia, and Salsola vermiculata-are associated with three species of gall midges. Erica arborea is the host plant with the highest number of gall midges: it hosts Dasineura ericaescopariae (Dufour, 1837), D. grasseti Barnes, 1935, Myricomyia mediterranea (Löw, 1885), and Wachtliella ericina (Löw, 1885). Zoogeographical analysis: 62 species (57%) are Mediterranean, 33 species (30%) European, ten species (8%) Eurosiberian; Micromya lucorum rondani, 1840, Cedrocrypta montana Kieffer, 1919 and Aphidoletes aphidimyza (Rondani, 1847) are Holarctic species; Mayetiola destructor (Say, 1817) is Palaearctic species. Economic importance: no significant pests in agriculture and forestry were recorded. Mayetiola destructor, M. hordei Kieffer, 1909, and M. avenae (Marchal, 1895) are potential pests of cereals.
... In this review, the fossil gall record is evaluated using three approaches that have been used in the primary literature to characterize galls. The first approach, historically the oldest, employs descriptions of galls as they were encountered in studies of fossil floras (Wittlake, 1981;Larew, 1986;Scott et al., 1994;Skuhravá and Skuhravý, 2009). Such descriptions of galls were made often by paleobotanists that noticed unusual structures on fossil (Mei et al., 1992) plants that could not be explained by known traits of plants (Van Amerom, 1973;Hickey and Doyle, 1977;Ash, 1997) but were consistent with known gall structures. ...
... Grasslands were associated with global aridification, although the timing of expansion varied from continent to continent (Edwards, 2010). In modern grasslands, the diversity of plant-insect interactions is associated with grasses (Tscharntke and Greiler, 1995) and includes external chewers (Hummelen and Gillon, 1968;Capinera and Roltsch, 1980;Quinn and Walgenbach, 1990), piercers and suckers (Hansen et al., 1985;Tscharntke, 1989), stem borers (Stiling and Strong, 1983;Moore and Clements, 1985), miners (Scheirs et al., 2001;Martin, 2007;Luginbill and Urbahns, 1916), and gallers (Ambrus and Hably, 1979;Price et al., 1987;Tscharntke, 1988Tscharntke, , 1994Zerova, 1978;Harris et al., 2003;De Bruyn, 2005;Skuhravá and Skuhravý, 2009;Nartshuk, 2014;Coelho et al., 2017). However, fossil galls are not associated with the fossil record of grasslands. ...
... Although there is a diversity of FFGs on modern grasses, gallers are an exception. When compared to dicots, few galler taxa occur on monocots in general and grasses in particular (Mani, 1964;Raman et al., 2005;Skuhravá and Skuhravý, 2009), a consequence that also is borne out in the fossil record where there is an absence of gallers on grasses throughout the dominant 34-millionyear-long history of this highly diverse clade (Supplementary Appendix 3). By contrast, miners-the other diverse endophytic group on vascular plants-are moderately abundant on grasses (Spencer, 1990). ...
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Insect and mite galls on land plants have a spotty but periodically rich and abundant fossil record of damage types (DTs), ichnotaxa, and informally described gall morphotypes. The earliest gall is on a liverwort of the Middle Devonian Period at 385 million years ago (Ma). A 70-million-year-long absence of documented gall activity ensues. Gall activity resumes during the Pennsylvanian Period (315 Ma) on vegetative and reproductive axial organs of horsetails, ferns, and probably conifers, followed by extensive diversification of small, early hemipteroid galler lineages on seed-plant foliage during the Permian Period. The end-Permian (P-Tr) evolutionary and ecological crisis extinguished most gall lineages; survivors diversified whose herbivore component communities surpassed pre-P-Tr levels within 10 million years in the mid-to late Triassic (242 Ma). During the late Triassic and Jurassic Period, new groups of galling insects colonized Ginkgoales, Bennettitales, Pinales, Gnetales, and other gymnosperms, but data are sparse. Diversifying mid-Cretaceous (125–90 Ma) angiosperms hosted a major expansion of 24 gall DTs organized as herbivore component communities, each in overlapping Venn-diagram fashion on early lineages of Austrobaileyales, Laurales, Chloranthales, and Eurosidae for the Dakota Fm (103 Ma). Gall diversification continued into the Ora Fm (92 Ma) of Israel with another 25 gall morphotypes, but as ichnospecies on a different spectrum of plant hosts alongside the earliest occurrence of parasitoid attack. The End-Cretaceous (K-Pg) extinction event (66 Ma) almost extinguished host–specialist DTs; surviving gall lineages expanded to a pre-K-Pg level 10 million years later at the Paleocene-Eocene Thermal Maximum (PETM) (56 Ma), at which time a dramatic increase of land surface temperatures and multiplying of atmospheric pCO2 levels induced a significant level of increased herbivory, although gall diversity increased only after the PETM excursion and during the Early Eocene Climatic Optimum (EECO). After the EECO, modern (or structurally convergent) gall morphotypes originate in the mid-Paleogene (49–40 Ma), evidenced by the Republic, Messel, and Eckfeld floras on hosts different from their modern analogs. During subsequent global aridification, the early Neogene (20 Ma) Most flora of the Czech Republic records several modern associations with gallers and plant hosts congeneric with their modern analogs. Except for 21 gall DTs in New Zealand flora, the gall record decreases in richness, although an early Pleistocene (3 Ma) study in France documents the same plant surviving as an endemic northern Iran but with decreasing associational, including gall, host specificity.
... Some have been exploited as a commercial supply of lye or potash, while others have served as important fuel sources [6,7]. Since many specimens lack the required characteristics for species identification, it has historically been challenging to identify collections because many members of this family are succulent and late in flowering and fruiting [8][9][10]. The primary quality of these plants is that they are especially resilient to saline environments and environmental stresses [11][12][13]. ...
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The genus Anabasis is a member of the family Amaranthaceae (former name: Chenopodiaceae) and includes approximately 102 genera and 1400 species. The genus Anabasis is one of the most significant families in salt marshes, semi-deserts, and other harsh environments. They are also renowned for their abundance in bioactive compounds, including sesquiterpenes, diterpenes, triterpenes, saponins, phenolic acids, flavonoids, and betalain pigments. Since ancient times, these plants have been used to treat various diseases of the gastrointestinal tract, diabetes, hypertension, and cardiovascular diseases and are used as an antirheumatic and diuretic. At the same time, the genus Anabasis is very rich in biologically active secondary metabolites that exhibit great pharmacological properties such as antioxidant, antibacterial, antiangiogenic, antiulcer, hypoglycemic, hepatoprotective, antidiabetic, etc. All of the listed pharmacological activities have been studied in practice by scientists from different countries and are presented in this review article to familiarize the entire scientific community with the results of these studies, as well as to explore the possibilities of using four plant species of the genus Anabasis as medicinal raw materials and developing medicines based on them.
... The olive leaf gall midge, Dasineura oleae (Angelini, 1831) (Diptera: Cecidomyiidae), attacks Olea europaea L. leaflets, young branches, and floral buds, inducing the formation of galls. This midge, endemic to the Mediterranean region, has been recorded in several countries in this area, including most of the largest olive producers [3]. Dasineura oleae was considered a sporadic pest [4] until recent reports of outbreaks [5][6][7][8]. ...
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Dasineura oleae was considered a minor pest in olive orchards. However, in the last decade, outbreaks have been reported all over its distribution area. Little is known about D. oleae biological control strategies; therefore, investigations into the biology and ecology of D. oleae parasitoids are urgently needed. In this scenario, the present field study reported the flight period of D. oleae parasitoids, evaluating their relative abundance over other parasitoids living in olive orchards. Furthermore, it estimated the effect of local and landscape features on D. oleae parasitoids within the frame of the overall parasitoid community. Lastly, we aimed to provide useful insights into the effectiveness of parasitoids for D. oleae population management. Hymenopteran parasitoids were sampled using Malaise traps in six sampling sites in central Italy. Results showed that Platygaster demades was the most abundant D. oleae parasitoid. Its presence was associated with high rates of D. oleae parasitism. The abundance of this parasitoid was influenced by the abundance of seminatural habitats.
... Although the origin of its host plant, C. dactylon, is not quite known, however this plant is widely distributed in the Oriental region, extends up to southern Europe and North Africa. Therefore, the gall midge O. cynodontis is evaluated as alien species in Europe (Skuhravá & Skuhravý, 2009;Skuhravá et al., 2010). By introducing these genus and species, the number of known gall midge fauna of Iran reaches 38 genera and 67 species. ...
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The larvae of Lasioptera donacis Coutin feed on fungal communities lining galleries within the mesophyll of leaf sheaths of Arundo donax in an aggregative manner. It has been stated that L. donacis could have established a fundamental symbiotic relationship with one fungus, although the fungal composition of these communities remains unsettled. Using a culture-dependent approach and ITS sequencing, the present work characterizes and compares the fungal communities associated with L. donacis in Eurasia with the endophytes of A. donax in Texas where L. donacis is absent. The 65 cultivable isolates obtained from L. donacis fungal communities were sorted into 15 MOTUs, among which Fusarium and Sarocladium predominated. No particular MOTU was systematically recovered from these communities regardless of the sites. The 19 isolates obtained in Texas were sorted into 11 MOTUs. Sarocladium and Fusarium were commonly found in Texas and Eurasia. Our finding indicate that the communities were composed of a diverse assemblage of non-systemic endophytes, rather than an exclusive fungal symbiont. From ovipositors and ovarioles of L. donacis emerging from plants in France, we opportunistically isolated the endophyte Apiospora arundinis, which lies at the origin of further research pertaining to its role in the feeding and oviposition of L. donacis.
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For the first time, a review of gall midges-inquilines, developing together with gall-formers, among which gall midges dominate is provided. In the world, 197 species of gall midges of 41 genera have been identified, in the galls of which 177 species of inquiline gall midges from 27 genera have been found. They are found on plants of 243 species of 160 genera of 53 families and 20 orders. The core of the gall-forming fauna is Cecidomyiinae – 118 species (59.9%) from 26 genera (63.4%), and the core of the inquiline fauna is Lasiopterinae: 63 species (32.0%) from 15 genera (36.6%). Ten common genera were identified, in which there are both inquilines and gall-formers. The proportion of inquilines in these genera is more than a third of the species, for Macrolabis – 39.1% (25 out of 64) and Camptoneuromyia – 86.7% (13 out of 15). Gall-formers and inquilines are predominantly narrow oligophages, specific in respect to the genus or family of the host plant, predominantly Fabaceae. Among gall-formers, the share of specific genera is 61.0% (25 out of 41), while among inquilines is 37.0% (10 out of 27). Host plants of the Rosids subclass are represented by 124 species (51.0%), 88 genera (55.0%) from 28 families (46.2%), most of which are trees and shrubs. Inquiline gall midges have been found in all zoogeographic regions; however no common species have been found. They dominate in the Palaearctic (118 species, 66.7% of 177) and Neotropical (40 species, 22.6%) regions. In the Nearctic region there are only 15 (8.5%) species. In the Palaearctic, inquiline species have been identified in 19 genera (70.4% of 27), of which 7 are endemic. In the Neotropical region, the inquilines belong to 7 genera (25.9%), with no endemics found. The core of the fauna with an abundance of endemic and widespread genera of inquilines formed in the Palaearctic region. In the gall midges, inquiline gall midges predominate, but inquilines develop from other taxonomic groups: insects (with a predominance of Cynipidae) and fungi. Inquilines present the potential for their gradual transition to gall formation and possible speciation during the assimilation of galls and plants of other species. In the galls of gall midges, inquilines actively influence the formation of galls and the development of the host larvae, contribute to their feeding, inhibit or lead to death. Key words : complexes of gall midges, specific genera, inquilines, gall-formers, endemics, host plants, evolution.
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This datasheet on Haplodiplosis marginata covers Identity, Overview, Distribution, Dispersal, Hosts/Species Affected, Diagnosis, Biology & Ecology, Environmental Requirements, Natural Enemies, Impacts, Uses, Prevention/Control, Further Information.
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Galls are structures of vegetal tissue modified by several biological agents, mainly dipterans of the Cecidomyiidae family. The galls are indicators of the gall inducers’ presence, because of the species-specific interaction between the gall inducer and its host plant species. The aim of this study was to expand the geographical distribution of cecidomyiids – usually known only to the type-locality – in species of Andira Lam. (Fabaceae) distributed in Brazil, through the presence of their gall morphotypes in host plants. We searched for records of gall morphotypes in Andira species in all inventories of insect galls in Brazilian biomes and in virtual herbaria in Brazilian and abroad institutions. We found six species of Andira with forty-nine registers of 20 morphotypes of galls induced by cecidomyiids. They were from 35 localities; of those, 15 Municipalities, five States and the Federal District are new points of occurrence. We found three new registers for the fusiform gall in A. fraxinifolia, four registers for the fusiform gall in A. humilis, two new registers for the lenticular gall in A. nitida, and six new registers for three morphotypes in A. vermifuga. No new records were found for the morphotypes of A. cujabensis and A. surinamensis. These results indicate that digital tools, combined with well-illustrated inventory data, are capable to expand knowledge about the distribution of cecidomyiids through the recognition of their specific marker, the morphotypes. Keywords: Andira fraxinifolia; Andira humilis; Andira nítida; Andira vermífuga; Insect-plant interaction
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Gall-inducing insects and mites are able to manipulate plant tissues to induce galls. As galling species are sessile, their sampling is relatively easy, but many aspects must be taken into account in order to adequately characterize galling fauna. Aspects related to the adoption of the methods for field sampling, standardization of gall morphotypes, and adequate photographic record of the galls are essential for a good sampling of galling arthropods. The adequate laboratory processing of host plants, as well as the treatment of galls to obtain gallers, and the subsequent identification of galling taxa are also important aspects for studies involving plant-galling interactions.
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Eight new species of gall midges of the genera Bryocrypta, Winnertzia, Brachineurina, Jaapiella, and Didymomyia are described from the Eocene Rovno amber.
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Contains a review of 320 gall-midge species ascertained in Poland. From the zoogeographical veiwpoint the most interesting species occur in the High Tatra regions on both the Polish and Czechoslovak sides: Jaapiella alpina (on Silene acaulis), Dasyneura alpestris (on Arabis alpina) and Dasyneura phyteumatis (on Phyteuma orniculare and Phyteuma spiceatum).-from English summary