Ferrantia - Trichoptera-RP
Ferrantia - Trichoptera-RP
Ferrantia - Trichoptera-RP
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<strong>Ferrantia</strong><br />
55<br />
Proceedings of the first conference<br />
on faunistics and zoogeography<br />
of European <strong>Trichoptera</strong><br />
Luxembourg<br />
2 nd - 4 th September 2005<br />
Marc Meyer<br />
Peter Neu<br />
(editors)<br />
Luxembourg, 2008<br />
Travaux scientifiques du Musée national d'histoire naturelle Luxembourg
Contents<br />
Proceedings of the first conference on faunistics and zoogeography of European<br />
<strong>Trichoptera</strong>. Luxembourg 2 nd - 4 th September 2005.<br />
Marc Meyer & Peter Neu (editors)<br />
The history and present state of <strong>Trichoptera</strong>research in the Czech Republic<br />
Chvojka Pavel, Komzák Petr 11<br />
The genus Rhyacophila Pictet, 1834 in Italy<br />
Fernanda Cianficconi, Carla Corallini, Barbara Todini 22<br />
Caddisfly assemblages characterizing different ecological areas in Luxembourg:<br />
from geographical distributions to bioindication<br />
Alain Dohet, Martial Ferréol, Henry-Michel Cauchie & Lucien Hoffmann 33<br />
Spatial and temporal distribution of <strong>Trichoptera</strong> larvae in the Mirusha River (Kosova)<br />
Agim Gashi, Halil Ibrahimi 57<br />
Limes norrlandicus - a natural biogeographical border for caddisflies (<strong>Trichoptera</strong>) in Sweden<br />
Bo Gullefors 61<br />
Distribution of caddisflies in The Netherlands<br />
Bert Higler 66<br />
State of knowledge of investigations on <strong>Trichoptera</strong> larvae in Kosova<br />
Halil Ibrahimi, Agim Gashi 70<br />
The <strong>Trichoptera</strong> (Insecta) of the Bán Stream, Bükk Mts., northern Hungary<br />
Ottó Kiss 73<br />
Glacial refugia of the montane caddisflyDrusus discolor (Rambur, 1842)<br />
Steffen U. Pauls, H. Thorsten Lumbsch, Peter Haase 80<br />
The Indicator Database for European Freshwater Invertebrates<br />
Astrid Schmidt-Kloiber, Wolfram Graf, Otto Moog, Armin Lorenz, Daniel Hering 85<br />
Checklist of the <strong>Trichoptera</strong> of the Grand Duchy of Luxembourg - First revision<br />
Isabel Schrankel, Peter J. Neu, Alain Dohet, Fernand Schoos 89<br />
Zoogeographical characteristics of the <strong>Trichoptera</strong> Fauna of Turkey<br />
Füsun Sipahiler 93<br />
First revision of the Romanian caddisflies (Insecta: <strong>Trichoptera</strong>)<br />
Part 1: Systematic checklist (updated: 12/2005)<br />
Lujza Ujvárosi, Sabina C. Robert, Peter J. Neu, Berthold Robert 110<br />
Zoogeographic division of Slovenia based on caddisfly distribution<br />
Gorazd Urbanič 125<br />
The larva of Micrasema cenerentola Schmid, 1952 (Insecta: <strong>Trichoptera</strong>: Brachycentridae)<br />
Rufino Vieira-Lanero, Marcos A. González, Fernando Cobo, Mª. José Servia 133<br />
Light-trapping of <strong>Trichoptera</strong> at the March, an eighth-orderAustrian lowland river<br />
Johann Waringer, Wolfram Graf 141<br />
Overall distributional patterns of European <strong>Trichoptera</strong><br />
Peter Wiberg-Larsen 143<br />
<strong>Ferrantia</strong> • 55 / 2008
First conference on faunistics and zoogeography<br />
of European <strong>Trichoptera</strong><br />
Luxembourg<br />
2 nd - 4 th September 2005<br />
Organising institution: ��s��� ��s��� �a�i��a�� �a�i��a�� ��his��i��� ��his��i��� �a������������� �a������������� ����������<br />
����������<br />
Venues: ��s��� �a�i��a�� ��his��i��� �a������������� ����������<br />
C�c��� H������ B����ai��� B���sch��i�-P��a���<br />
Administrative responsibility: G�������s B��ch���. Di���c���<br />
Scientific responsibility: �a�c ���y����� C��s���va��� �f ���p�. Z������y �f<br />
I�v��������a���s.<br />
Scientific committee: P��f. P��f. D�. D�. Ha�s Ha�s �a��ic�y�� �a��ic�y�� �i��� �i��� ��� ���<br />
D�. W���f�a� ���y�� B�����i� �D�<br />
P��f. D�. �a�c� G����a����s�� �a��i� �E�<br />
P��f. D�. J�ha�� Wa�i������� Wi��� ���<br />
D�. ���s Uh�����vich�� P�cs �H�<br />
Organising committee: �a�c ���y����� ��h���� ����������� ���<br />
P������ N����� Bi����� �D��<br />
Isa����� �ch�a�������� �ch�a���������� ��������ach ��������ach ��������ach ����� ����� ����� s��c����a�y s��c����a�y s��c����a�y s��c����a�y
Preface of the editors<br />
I� was P������ N��� N��� wh� wh� wh� ha� ha� ha� �h�� �h�� �h�� i���a i���a i���a �� �� �� ���a�is�� ���a�is�� ���a�is�� ���a�is��<br />
a first European conference on caddisflies<br />
�T�ich�p����a�. H�� as���� �h�� a��h�� if �his ��v����<br />
c����� ��� h����� i� ����������. Wi�h �h�� s�pp���<br />
�f �h�� Di���c��� �f ��� ��s���� a�� �h�� f���i��<br />
�f �h�� Na�i��a�� R��s��a�ch F��� �FNR� �h�� p��j��c�<br />
c����� s�a��. Th�� ai� �f �his i�i�ia�iv�� was �� c���a���<br />
a c�����ica�i�� p��a�f��� f�� T�ich�p���������is�s<br />
�� a c���i�����a�� ����v����.<br />
Th�� c��f������c�� ha� a ���� s�cc��ss�� wi�h a ���a�� �f<br />
62 pa��icipa��s f��� 19 �a�i��s�� 16 ����c�����s a�� 11<br />
p�s����s. Th�� fac� �ha� �h�� v������ was a C��f������c��-<br />
H������ i� �h�� ����h �f ������������ ���a� �h�� �iv���<br />
Sure, one of the less polluted flowing water in<br />
C�����a�� E���p�� �av�� �h�� �pp�����i�y f�� �h��<br />
participants to collect caddisflies, particularly<br />
wi�h �h�� �s�� �f ��i�h� ��aps s��� a����� �h�� v������.<br />
U�a�i���s��y �h�� pa��icipa��s a������� �� p����c�� a<br />
p����ica�i�� wi�h �h�� p��c�����i��s �f �h�� c��f������c��.<br />
After a long and somehow time-consuming task,<br />
w�� a��� p����as��� �� p����ish �h��s�� p��c�����i��s i�<br />
�his v������� �f ��� ������aphic s���i��s�� F����a��ia.<br />
The first chapter brings the programme of the<br />
c��f������c��.<br />
The scientific contributions follow in alphabetic<br />
������ �f �h�� a��h��s� �a���s.<br />
Acknowledgments<br />
Fi�s��� w�� hav�� �� �ha�� G�������s B��ch����� Di���c���<br />
of the MnhnL for the support, the financial help<br />
a�� �h�� s�p���� s�cia�� p����a����. Th�� ���a�is���s<br />
�ha�� �h�� Na�i��a�� R��s��a�ch F��� �FNR� f�� �h��<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
s��s�a��ia�� f���i���� which a�����w��� �s �� i�vi���<br />
���y����� sp��a����s ��� f������ �y i�s�i���i��s ��<br />
��a��� ���h��i�i��s i� �h��i� c�����i��s.<br />
Th�� ���i���s a��� v���y ��a���f��� �� Isa����� �ch�a������<br />
wh� ���� ca��� �f �h�� �i����s� pa�� �f �h�� ���a�isi��<br />
�as�. W�� a��� ��a���f��� �ha� ��������s c�������a����s<br />
f��� ��� ��s���� ass����� �a�y i�p���a�� �as�s��<br />
��i��� �h�� ����i�� �f �h�� ���c��p�i�� ���s��� �h�� s���vic��s<br />
f�� pa��icipa��s�� �h�� ���ch�ica�� s�pp��� a���� ��as� ���<br />
least, the arranging of an excellent buffet on the<br />
first evening. We are also very grateful towards<br />
�i����� Bac���s�� h��a� �f ��� ��s�����aph���s<br />
s���vic���� f�� �h�� c��c��p��a�� ���si�� �f �h�� ����� a��<br />
�h�� c��f������c�� ��c������s.<br />
W�� a��s� �ha�� �h�� a��h��s f�� �h��i� c����i���i��s<br />
a�� �h�� a���y���s ���vi��w���s f�� �h�� c��p�������<br />
a�� c��s���c�iv�� c�������s a�� c�i�ics.<br />
W�� a��� i��������� �� Thi����y H�����i����� f�� �h��<br />
configuration and Romain Bei for the layout of<br />
�his iss���<br />
�a�c ���y��� a�� P������ N����� 21.03.2008<br />
7
8<br />
<strong>Ferrantia</strong> • 55 / 2008
Conference programme<br />
Friday, 2 nd September 2005<br />
Über den Stand der Faunistik und Zoogeografie<br />
���� T�ich�p������� i� E���pa �Ha�s �a��ic�y�<br />
Fi�s� i�����i� ���p��� �� �h�� a���as �f �is��i���i�� �f<br />
�h�� E���p��a� T�ich�p����a ��icha���� �a��ic�y�� P������<br />
J. N����<br />
Overall distributional patterns of European<br />
T�ich�p����a �P������ Wi������a�s����<br />
Th�� T�ich�p����a �f �h�� G�a�� D�chy �f �����������<br />
�Isa����� �ch�a������ ��� a��.�<br />
Specific caddisfly assemblages characterizing<br />
different ecological areas in Luxembourg: from<br />
������aphica�� �is��i���i��s �� �i�i��ica�i�� ����ai�<br />
D�h��� ��� a��.�<br />
Distribution of caddisflies in The Netherland: use<br />
a�� pi�fa����s �B���� Hi�������<br />
Saturday, 3 rd September 2005<br />
Z��������aphic �ivisi�� �f ����v���ia �as��� ��<br />
caddisfly distribution (Urbanic Gorazd)<br />
�i���s N�����a��ic�s - a �a���a�� �i�������aphica��<br />
border for caddisflies (<strong>Trichoptera</strong>) in Sweden (Bo<br />
G�������f��s�<br />
Z��������aphica�� cha�ac����is�ics �f �h�� T�ich�p����a<br />
Fa��a �f T�����y �Füs�� �ipahi������<br />
��a��� �f ���w�������� �f i�v��s�i�a�i��s �� T�ich�p����a<br />
i� U��ai��� �E�����a Dya����va<br />
The first electronically database of the Romanian<br />
T�ich�p����a�� wi�h a� a����a���� ��is� �f �h�� sp��ci��s<br />
���j��a Ujva��si�<br />
Sunday, 4 th September 2005<br />
Va�ia�i��i�y a�� �is��i���i�� �f sp��ci��s ��������i��<br />
�� �h�� Cha����p����y� vi�����sa ����p �T�ich�p����a;<br />
�i����phi��i�a��� i� E���p�� �Ka�a���y�a �aj��c�a�<br />
Fi�s� ���c��� �f �h�� sp��ci��s Hy���psych�� Hy���psych�� i�c���i�a i�c���i�a i�c���i�a<br />
i� R��a�ia�� wi�h sp��cia�� ���f������c�� �� i�s ��c�����ica��<br />
���q�i��������s ��i����s Ba��i��� Ba��i���<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Phylogeography of the montane caddisfly<br />
Drusus discolor (Rambur, 1842) (<strong>Trichoptera</strong>:<br />
Limnephilidae, Drusinae) (Steffen Pauls et al.)<br />
I�v��s�i�a�i��s �� W���a���ia �ccipi�a��is PICTET<br />
1834 �P������ J. N����<br />
Ca��is ��a�va�� i� ���a�i��a�i�� ��a�i���� ����ch<br />
Pi������a��� ��a�is _ aw C��ach���ws�i�<br />
E���a-����i�����a���a� c�������s �f a���as �f T�ich�p����a<br />
�f �h�� E���p��a� Di���a�� �Ha�s �a��ic�y�<br />
Posters<br />
Th�� ��a�va �f Micrasema cenerentola �CH�ID�� 19�2 19�2<br />
(<strong>Trichoptera</strong>: Brachycentridae) (Marcos Gonzalez<br />
��� a��.�<br />
T�ich�p����a �f �a��scap�� Pa�� W�������aDy����ws�i��<br />
W�������a Dy����ws�i��<br />
�Dy����ws�i�� Hi����s� ��a��a ����� ��� a��.�<br />
Caddisflies (Insecta: <strong>Trichoptera</strong>) of Mazovia and<br />
P����asi�� �P���a��� - s�a��� �f ���w�������� �Wi�����<br />
���c����pa�s�i�<br />
Towards a Red Data Book of the Swiss caddisfly<br />
fa��a �I�s��c�a�� T�ich�p����a� �V������a ���i�i -<br />
F�����i��� H��i��ich Vic����i�i�<br />
His���y a�� ���s����s �f T�ich�p����a ���s��a�ch �f<br />
caddisfly fauna in the Czech Republic (Pavel<br />
Chv�j�a�� P���� K�����<br />
�i�h�-��appi�� �f T�ich�p����a a� �h�� �a�ch�� a<br />
���w��a�� �iv��� i� Eas����� ��s��ia �J�ha�� Wa�i�������<br />
W���f�a� G�af�<br />
The caddisflies of Vorarlberg (Austria): a meeting<br />
p��ac�� f�� va�i��s ����������aphic �����������s<br />
�W���f�a� G�af�� J�ha�� Wa�i������<br />
T�ich�p����a �I�s��c�a� �f �h�� Ba� s����a��� Bü�� ��s.��<br />
northern Hungary (Otto Kiss)<br />
Rhyac�phi��a Pic������ 1834 i� I�a��y �F����a��a<br />
Cianficconi et al.)<br />
The caddisflies (<strong>Trichoptera</strong>) of Suwalki Lakeland<br />
�N-E P���a��� - c������p��a�y �a�a �Ja��s�� �aj��c�i��<br />
B���is��aw ���c����s�y�<br />
T�ich�p���������ica�� i�v��s�i�a�i��s i� �h�� �W<br />
U��ai��� �E�����a Dya����va�<br />
www.f���shwa������c�����y.i�f� - � �a�a�as�� f��<br />
�i�i��ica���s �f aq�a�ic ��c�sys����s ��s��i�<br />
�ch�i��-K���i���� ��� a��.�<br />
9
10<br />
<strong>Ferrantia</strong> • 55 / 2008
P. Chvojka, P. Komzák The history and present state of <strong>Trichoptera</strong> research in the Czech Republic<br />
The history and present state of <strong>Trichoptera</strong><br />
research in the Czech Republic<br />
Th�� his���y �f �h�� ��ich�p���������ica�� ���s��a�ch wi�hi� �h��<br />
�����i���y �f �h�� p���s���� C����ch R��p����ic is s���a�i�����.<br />
The first data on <strong>Trichoptera</strong> in Bohemia, Moravia and<br />
�h�� s���h���� pa�� �f �i����sia �a��� �ac� �� �h�� �i������ �f �h��<br />
19�h c������y �K������a�i�� ����i��. This a�� a���� s��s��q�����<br />
i�p���a�� p���i��s a�� p���s��a��i�i��s �f ��ich�p���������ica��<br />
research are briefly presented.<br />
�cc���i�� �� ��� p���s���� ���w���������� 2�2 sp��ci��s w�����<br />
���c������ f��� �h�� �����i���y �f �h�� C����ch R��p����ic �243<br />
a�� 211 f��� B�h���ia a�� ���avia�� ���sp��c�iv����y�<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Chvojka Pavel<br />
D��pa������� �f E���������y<br />
Na�i��a�� ��s������ K���a�ic�� 1<br />
CZ-148 00 P�aha 4�� C����ch R��p����ic<br />
pav����_chv�j�a@��.c��<br />
Komzák Petr<br />
Institute of Botany and Zoology<br />
Faculty of Science, Masaryk University<br />
Kotlářská 2<br />
CZ-611 37 Brno, Czech Republic<br />
komzak@email.cz<br />
Keywords: <strong>Trichoptera</strong>, faunistics, new records, Czech Republic, Bohemia, Moravia<br />
Abstract<br />
History<br />
The first data on <strong>Trichoptera</strong> within the territory<br />
�f �h�� p���s���� C����ch R��p����ic �a��� �ac� �� �h��<br />
�i������ �f �h�� 19�h c������y. I� his p����ica�i��s<br />
�1848�� 18�8a�� ��� 18�9a�� ��� 1860� K������a�i ��is�s �����<br />
�ha� 70 sp��ci��s �f T�ich�p����a f��� B�h���ia a��<br />
���avia �i�c����i�� �h�� s���h���� pa�� �f �i����sia�� i.��.<br />
f������ Ös�������ichisch �ch����si����. ����i� �1873�� 1874�<br />
a����� a���h��� 9 sp��ci��s f��� �h�� J��s���í�y ��s.<br />
More detailed knowledge of the caddisfly fauna of<br />
B�h���ia was ���ai���� a� �h�� ���� �f �h�� 19�h c������y<br />
���� �� �h�� w��� �f F. K��ap������ wh� a��s� p����ish���<br />
the first list of Bohemian <strong>Trichoptera</strong> (1890). He<br />
s��s��q�������y c��p������������ i� �K��ap���� 1891-<br />
1903� a�� ���i�� �his p���i�� �h�� ������� �f sp��ci��s<br />
���w� f��� B�h���ia a�� ���avia i�c���as��� f���<br />
���i�� �h�� ��as� 1�0 y��a�s. H�w��v����� 9 sp��ci��s hav��<br />
��� ������ f���� si�c�� �h�� �i������ �f �h�� 20�h c������y��<br />
�h�����f���� �h��y a��� c��si������� �� ��� ����i��a����y ����i�c�<br />
(RE). Of extant species, 31 % are qualified as threatened<br />
�19 a��� c�i�ica����y ����a�������� - CR�� 26 ����a�������� - EN��<br />
a�� 30 v�������a����� - VU�.<br />
Th�� ac��a�� ch��c���is� �f C����ch T�ich�p����a �i�c����i��<br />
���w ���c���s �f Rhyac�phi��a ��a��vis Pic���� a�� Hy���p�i��a<br />
vich�aspa �ch�i�� is p���s������� a�� �h�� �h���a� ca������i��s<br />
RE�� CR�� EN�� VU a��� i��ica����.<br />
1�0 �� 189. Th����� ��h��� sp��ci��s w����� �����i�����<br />
f��� B�h���ia �y Šá�a�� �1920�.<br />
� f���h��� i�p���a�� p���i�� w����� �h�� 1930s�� wh���<br />
K. �ay��� p����ish��� his fa��is�ic c����i���i��s<br />
a�� �h�� ch��c���is� �f T�ich�p����a �f �h�� f������<br />
C����ch�s���va�ia ��ay��� 1939� wi�h 204 sp��ci��s<br />
f��� B�h���ia a�� ���avia. I� �h�� s��c��� ha��f<br />
�f �h�� 20�h c������y�� F. K��av��c�� K. N�v�� �. O����<br />
F. P�����š�a�� E. ������á� a�� J. �ý���a c��si����a���y<br />
extended the knowledge of caddisfly distribution<br />
i� �h�� C����ch R��p����ic. F���h��� �a�a�� �as���<br />
�� ca��is ��a�va���� ���s������� f��� ��������s<br />
hy����i�����ica�� s���i��s �s���� ��.�. O�� 1969�. N��w<br />
�a�i��a�� a�� ����i��a�� ���c���s w����� i�c������� i� �h��<br />
�p�a���� ��is� �f C����ch�s���va� T�ich�p����a �N�vá�<br />
& O�� 1977�; a ���a�� �f 224 sp��ci��s w����� �����i�����<br />
f��� B�h���ia a�� ���avia.<br />
11
P. Chvojka, P. Komzák The history and present state of <strong>Trichoptera</strong> research in the Czech Republic<br />
12<br />
Intensive field samplings conducted mainly in<br />
�a����� p�����c�i�� a���as w����� ca��i��� ��� i� �h�� 1990s��<br />
a�� s��v���a�� pap���s wi�h ���w ���c���s �f T�ich�p����a<br />
f�� �h�� �����i���y �f B�h���ia a��/�� ���avia w�����<br />
p����ish��� �����p 1990�� Chv�j�a 1996�� ������á� 1999�.<br />
New findings and results of the revision of earlier<br />
�a�a w����� s���a�i����� �y Chv�j�a & N�vá� �2001�.<br />
The latest new records of caddisflies were obtained<br />
from Moravia (Komzák 2001, Němcová 2001, Sedlák<br />
2001, Komzák & Chvojka 2005, Komzák, Kroča &<br />
B�j��vá 2006��� si�c�� ��ich�p���������ica�� ���s��a�ch<br />
was f�c�s��� �� s���� pa��s �f ���avia which w�����<br />
omitted in the past.<br />
Results<br />
�cc���i�� �� ��� p���s���� ���w���������� 2�2 sp��ci��s<br />
w����� ���c������ f��� �h�� �����i���y �f �h�� C����ch<br />
R��p����ic �243 a�� 211 f��� B�h���ia a�� ���avia��<br />
���sp��c�iv����y� ���i�� �h�� ��as� 1�0 y��a�s �Ta�. 1�.<br />
H�w��v����� 9 sp��ci��s hav�� ��� ������ c�������c���� si�c��<br />
�h�� �i������ �f �h�� 20�h c������y�� �h�����f���� �h��y<br />
a��� c��si������� �� ��� ����i��a����y ����i�c�. Of ����a��<br />
species, 31 % are qualified as threatened (19 are<br />
c�i�ica����y ����a���������� 26 ����a���������� a�� 30<br />
v�������a������ �Chv�j�a�� N�vá� & ������á� 200��.<br />
Table 1. Checklist of <strong>Trichoptera</strong> of the Czech Republic (Taxa are listed according to Malicky 2005).<br />
B = Bohemia, M = Moravia<br />
Threat category Czech Republic<br />
Rhyacophilidae<br />
Rhyacophila dorsalis persimilis �c�ach��a��� 1879 B<br />
Rhyacophila evoluta �c�ach��a��� 1879 B<br />
Rhyacophila fasciata Ha������ 18�9 B �<br />
Rhyacophila glareosa �c�ach��a��� 1867 B �1 Rhyacophila hirticornis �c�ach��a��� 1879 VU B<br />
**Rhyacophila laevis Pic������ 1834 EN B<br />
Rhyacophila mocsaryi K��ap������ 1898 VU �<br />
Rhyacophila nubila (Zetterstedt, 1840) B �<br />
Rhyacophila obliterata �c�ach��a��� 1863 B �<br />
Rhyacophila pascoei �c�ach��a��� 1879 RE B<br />
Rhyacophila philopotamoides �c�ach��a��� 1879 VU B �<br />
Rhyacophila polonica �c�ach��a��� 1879 B �<br />
Rhyacophila praemorsa �c�ach��a��� 1879 B<br />
Rhyacophila pubescens Pic������ 1834 B �2 Rhyacophila torrentium Pic������ 1834 VU B �<br />
Rhyacophila tristis Pic������ 1834 B �<br />
Rhyacophila vulgaris Pic������ 1834 B �<br />
Glossosomatidae<br />
Glossosoma boltoni C���is�� 1834 B �<br />
Glossosoma conformis N����iss�� 1963 B �<br />
Glossosoma intermedium �K��ap������ 1892� B �<br />
Agapetus delicatulus �c�ach��a��� 1884 CR B �<br />
Agapetus fuscipes C���is�� 1834 B �<br />
Agapetus laniger �Pic������ 1834� EN B �<br />
Agapetus ochripes C���is�� 1834 B �<br />
Synagapetus armatus ��c�ach��a��� 1879� VU � 2<br />
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P. Chvojka, P. Komzák The history and present state of <strong>Trichoptera</strong> research in the Czech Republic<br />
Threat category Czech Republic<br />
Synagapetus iridipennis �c�ach��a��� 1879 B �<br />
Synagapetus moselyi �U�������� 1938� VU B �<br />
Ptilocolepidae<br />
Ptilocolepus granulatus �Pic������ 1834� B<br />
Hydroptilidae<br />
Hydroptila angulata ��s����y�� 1922 B � 2<br />
Hydroptila angustata ��s����y�� 1939 CR B<br />
Hydroptila forcipata �Ea����� 1873� B �<br />
Hydroptila lotensis ��s����y�� 1930 � 2<br />
Hydroptila martini �a�sha������ 1977 VU B<br />
Hydroptila occulta �Ea����� 1873� CR B<br />
Hydroptila pulchricornis Pic������ 1834 B �<br />
Hydroptila simulans ��s����y�� 1920 B<br />
Hydroptila sparsa C���is�� 1834 B �<br />
Hydroptila taurica �a��y��v�� 1934 CR B<br />
Hydroptila tineoides Da���a��� 1819 CR B<br />
Hydroptila valesiaca �ch�i��� 1947 EN B<br />
Hydroptila vectis C���is�� 1834 VU B �<br />
**Hydroptila vichtaspa �ch�i��� 19�9 CR �<br />
Ithytrichia lamellaris Ea����� 1873 B �<br />
Orthotrichia angustella ��c�ach��a��� 186�� RE B<br />
Orthotrichia costalis �C���is�� 1834� B �<br />
Orthotrichia tragetti ��s����y�� 1930 EN B � 2<br />
Allotrichia pallicornis �Ea����� 1873� CR B � 3<br />
Agraylea multipunctata C���is�� 1834 B �<br />
Agraylea sexmaculata C���is�� 1834 B �<br />
Tricholeiochiton fagesii �G�i�a���� 1879� VU B �<br />
Oxyethira falcata �������� 1893 EN B<br />
Oxyethira flavicornis �Pic������ 1834� B �<br />
Oxyethira frici K��ap������ 1891 CR B � 2<br />
Oxyethira simplex Ris�� 1897 EN B<br />
Oxyethira tristella K��ap������ 189� RE B<br />
Philopotamidae<br />
Wormaldia copiosa ��c�ach��a��� 1868� EN B � 4<br />
Wormaldia occipitalis �Pic������ 1834� B �<br />
Wormaldia pulla ��c�ach��a��� 1878� VU B �<br />
Wormaldia subnigra �c�ach��a��� 186� CR B �<br />
Philopotamus ludificatus �c�ach��a��� 1878 B �<br />
Philopotamus montanus �D���va��� 1813� B �<br />
Philopotamus variegatus ��c�p���i�� 1763� B �<br />
Chimarra marginata ��i��a���s�� 1767� RE B �<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
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P. Chvojka, P. Komzák The history and present state of <strong>Trichoptera</strong> research in the Czech Republic<br />
14<br />
Threat category Czech Republic<br />
Ecnomidae<br />
Ecnomus tenellus �Ra������ 1842� B �<br />
Polycentropodidae<br />
Holocentropus dubius �Ra������ 1842� B �<br />
Holocentropus picicornis �����ph���s�� 1836� B �<br />
Holocentropus stagnalis �����a��a�� 1874� VU B �<br />
Cyrnus crenaticornis �K������a�i�� 18�9� EN B �<br />
Cyrnus flavidus �c�ach��a��� 1864 B �<br />
Cyrnus insolutus �c�ach��a��� 1878 VU B<br />
Cyrnus trimaculatus �C���is�� 1834� B �<br />
Polycentropus flavomaculatus �Pic������ 1834� B �<br />
Polycentropus irroratus �C���is�� 183�� VU B �<br />
Neureclipsis bimaculata ��i��a���s�� 17�8� B �<br />
Plectrocnemia brevis �c�ach��a��� 1871 B �<br />
Plectrocnemia conspersa �C���is�� 1834� B �<br />
Plectrocnemia geniculata �c�ach��a��� 1871 VU B �<br />
Psychomyiidae<br />
Lype phaeopa �����ph���s�� 1836� B �<br />
Lype reducta �Ha������ 1868� B �<br />
Psychomyia pusilla �Fa��ici�s�� 1781� B �<br />
Tinodes dives �Pic������ 1834� EN B<br />
Tinodes kimminsi �ý���a�� 1962 CR B<br />
Tinodes maclachlani Ki��i�s�� 1966 CR B<br />
Tinodes pallidulus �c�ach��a��� 1878 B �<br />
Tinodes rostocki �c�ach��a��� 1878 B �<br />
Tinodes unicolor �Pic������ 1834� B �<br />
Tinodes waeneri ��i��a���s�� 17�8� B �<br />
Hydropsychidae<br />
Cheumatopsyche lepida �Pic������ 1834� B �<br />
Hydropsyche angustipennis �C���is�� 1834� B �<br />
Hydropsyche botosaneanui Marinković-Gospodnetić, 1966 VU B<br />
Hydropsyche bulbifera �c�ach��a��� 1878 B �<br />
Hydropsyche bulgaromanorum �a��ic�y�� 1977 B �<br />
Hydropsyche contubernalis �c�ach��a��� 186� B �<br />
Hydropsyche dinarica Marinković-Gospodnetić, 1979 VU B<br />
*Hydropsyche exocellata D�f����� 1841 VU B �<br />
*Hydropsyche fulvipes �C���is�� 1834� EN B �<br />
Hydropsyche guttata Pic������ 1834 VU B<br />
Hydropsyche incognita Pi�sch�� 1993 B �<br />
Hydropsyche instabilis �C���is�� 1834� B �<br />
Hydropsyche modesta Navás�� 192� �<br />
Hydropsyche pellucidula �C���is�� 1834� B �<br />
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P. Chvojka, P. Komzák The history and present state of <strong>Trichoptera</strong> research in the Czech Republic<br />
Threat category Czech Republic<br />
Hydropsyche saxonica �c�ach��a��� 1884 B �<br />
Hydropsyche silfvenii U�������� 1906 B<br />
Hydropsyche siltalai Döh������� 1963 B �<br />
Hydropsyche tenuis Navás�� 1932 EN B<br />
Phryganeidae<br />
Agrypnia obsoleta ��c�ach��a��� 186�� VU B �<br />
Agrypnia pagetana C���is�� 183� VU B �<br />
*Agrypnia varia �Fa��ici�s�� 1793� B �<br />
Hagenella clathrata �K������a�i�� 1848� EN B �<br />
Oligostomis reticulata ��i��a���s�� 1761� VU B �<br />
Oligotricha striata ��i��a���s�� 17�8� B �<br />
Trichostegia minor �C���is�� 1834� B �<br />
Phryganea bipunctata R�����i�s�� 1783 B �<br />
Phryganea grandis �i��a���s�� 17�8 B �<br />
Brachycentridae<br />
Brachycentrus maculatus �F���c��y�� 178�� VU B �<br />
Brachycentrus montanus K��ap������ 1892 B �<br />
Brachycentrus subnubilus C���is�� 1834 B �<br />
Micrasema longulum �c�ach��a��� 1876 B �<br />
Micrasema minimum �c�ach��a��� 1876 B �<br />
Micrasema setiferum �Pic������ 1834� EN B �<br />
Goeridae<br />
Goera pilosa �Fa��ici�s�� 177�� B �<br />
Lithax niger �Ha������ 18�9� B �<br />
Lithax obscurus �Ha������ 18�9� VU B �<br />
Silo nigricornis �Pic������ 1834� B �<br />
Silo pallipes �Fa��ici�s�� 1781� B �<br />
Silo piceus �B�a������ 18�7� B �<br />
Lepidostomatidae<br />
Lepidostoma basale �K������a�i�� 1848� B �<br />
Lepidostoma hirtum �Fa��ici�s�� 177�� B �<br />
Crunoecia irrorata �C���is�� 1834� B �<br />
Limnephilidae<br />
Dicosmoecinae<br />
Ironoquia dubia �����ph���s�� 1837� B �<br />
Apataniinae<br />
Apatania fimbriata �Pic������ 1834� B �<br />
Apatania muliebris �c�ach��a��� 1866 RE B<br />
Drusinae<br />
Anomalopterygella chauviniana �����i��� 1874� B �<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
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P. Chvojka, P. Komzák The history and present state of <strong>Trichoptera</strong> research in the Czech Republic<br />
16<br />
Threat category Czech Republic<br />
Ecclisopteryx dalecarlica K������a�i�� 1848 B �<br />
Ecclisopteryx guttulata �Pic���� 1834� B<br />
Ecclisopteryx madida ��c�ach��a��� 1867� B �<br />
Drusus annulatus �����ph���s�� 1837� B �<br />
Drusus biguttatus �Pic������ 1834� EN B �<br />
Drusus discolor �Ra������ 1842� B �<br />
Drusus trifidus ��c�ach��a��� 1868� B �<br />
Limnephilinae: Limnephilini<br />
Anabolia brevipennis �C���is�� 1834� B �<br />
Anabolia furcata B�a������ 18�7 B �<br />
Anabolia nervosa �C���is�� 1834� B<br />
Glyphotaelius pellucidus �R�����i�s�� 1783� B �<br />
Grammotaulius nigropunctatus �R�����i�s�� 1783� B �<br />
Grammotaulius nitidus ��ü��������� 1764� EN B �<br />
Limnephilus affinis C���is�� 1834 B �<br />
Limnephilus algosus ��c�ach��a��� 1868� EN B<br />
Limnephilus auricula C���is�� 1834 B �<br />
Limnephilus binotatus C���is�� 1834 CR B �<br />
Limnephilus bipunctatus C���is�� 1834 B �<br />
Limnephilus centralis C���is�� 1834 B �<br />
Limnephilus coenosus C���is�� 1834 B �<br />
Limnephilus decipiens �K������a�i�� 1848� B �<br />
Limnephilus elegans C���is�� 1834 VU B �<br />
Limnephilus extricatus �c�ach��a��� 186� B �<br />
Limnephilus flavicornis �Fa��ici�s�� 1787� B �<br />
Limnephilus fuscicornis Ra������ 1842 VU B �<br />
Limnephilus germanus �c�ach��a��� 187� EN B<br />
Limnephilus griseus ��i��a���s�� 17�8� B �<br />
Limnephilus hirsutus �Pic������ 1834� B �<br />
Limnephilus ignavus �c�ach��a��� 186� B �<br />
Limnephilus incisus C���is�� 1834 VU B �<br />
Limnephilus lunatus C���is�� 1834 B �<br />
Limnephilus nigriceps (Zetterstedt, 1840) B �<br />
Limnephilus politus �c�ach��a��� 186� B �<br />
Limnephilus rhombicus ��i��a���s�� 17�8� B �<br />
Limnephilus sericeus ��ay�� 1824� B<br />
Limnephilus sparsus C���is�� 1834 B �<br />
Limnephilus stigma C���is�� 1834 B �<br />
Limnephilus subcentralis B�a������ 18�7 B �<br />
Limnephilus vittatus �Fa��ici�s�� 1798� B �<br />
Nemotaulius punctatolineatus �R�����i�s�� 1783� CR B<br />
Rhadicoleptus alpestris �K������a�i�� 1848� B �<br />
Limnephilinae: Chaetopterygini<br />
Annitella obscurata ��c�ach��a��� 1876� B �<br />
Annitella thuringica �U�������� 1909� VU B �<br />
<strong>Ferrantia</strong> • 55 / 2008
P. Chvojka, P. Komzák The history and present state of <strong>Trichoptera</strong> research in the Czech Republic<br />
Threat category Czech Republic<br />
Chaetopterygopsis maclachlani ����i��� 1874 B �<br />
Chaetopteryx fusca B�a������ 18�7 � 2<br />
Chaetopteryx major �c�ach��a��� 1876 B �<br />
Chaetopteryx polonica Dziędzielewicz, 1889 VU �<br />
Chaetopteryx villosa �Fa��ici�s�� 1798� B �<br />
Pseudopsilopteryx zimmeri ��c�ach��a��� 1876� B �<br />
Psilopteryx psorosa psorosa �K������a�i�� 1860� B �<br />
Psilopteryx psorosa bohemosaxonica ���y & B���sa���a���� 198� B<br />
Limnephilinae: Stenophylacini<br />
Acrophylax vernalis Dziędzielewicz, 1912 EN B<br />
Acrophylax zerberus B�a������ 1867 EN B<br />
Allogamus auricollis �Pic������ 1834� B �<br />
Allogamus uncatus �B�a������ 18�7� B �<br />
Halesus digitatus ��ch�a���� 1781� B �<br />
Halesus radiatus �C���is�� 1834� B �<br />
Halesus rubricollis �Pic������ 1834� B �<br />
Halesus tessellatus �Ra������ 1842� B �<br />
Hydatophylax infumatus ��c�ach��a��� 186�� B �<br />
Melampophylax nepos ��c�ach��a��� 1880� B �<br />
Micropterna lateralis �����ph���s�� 1837� B �<br />
Micropterna nycterobia �c�ach��a��� 187� B �<br />
Micropterna sequax �c�ach��a��� 187� B �<br />
Micropterna testacea �G�����i��� 1789� B �<br />
Parachiona picicornis �Pic������ 1834� B �<br />
Potamophylax carpathicus (Dziędzielewicz, 1912) VU �<br />
Potamophylax cingulatus cingulatus �����ph���s�� 1837� B �<br />
Potamophylax cingulatus alpinus T��ias�� 1994 B �<br />
Potamophylax cingulatus depilis Szczęsny, 1994 �<br />
Potamophylax latipennis �C���is�� 1834� B �<br />
Potamophylax luctuosus (Piller & Mitterpacher, 1783) B �<br />
Potamophylax nigricornis �Pic������ 1834� B �<br />
Potamophylax rotundipennis �B�a������ 18�7� B �<br />
Stenophylax permistus �c�ach��a��� 189� B �<br />
Stenophylax vibex �C���is�� 1834� VU B �<br />
Sericostomatidae<br />
Oecismus monedula �Ha������ 18�9� B �<br />
Sericostoma personatum ��p���c���� 1826� B �<br />
Sericostoma schneiderii �K������a�i�� 1848� B �<br />
Notidobia ciliaris ��i��a���s�� 1761� B �<br />
Odontoceridae<br />
Odontocerum albicorne ��c�p���i�� 1763� B �<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
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P. Chvojka, P. Komzák The history and present state of <strong>Trichoptera</strong> research in the Czech Republic<br />
18<br />
Threat category Czech Republic<br />
Molannidae<br />
Molanna angustata C���is�� 1834 B �<br />
Molanna nigra (Zetterstedt, 1840) CR B<br />
Molannodes tinctus (Zetterstedt, 1840) EN B �<br />
Beraeidae<br />
Beraea maurus �C���is�� 1834� B �<br />
Beraea pullata �C���is�� 1834� B �<br />
Beraeodes minutus ��i��a���s�� 1761� B �<br />
Beraeamyia hrabei �ay����� 1937 EN �<br />
Ernodes articularis �Pic������ 1834� B �<br />
Ernodes vicinus ��c�ach��a��� 1879� EN B � 2<br />
Leptoceridae<br />
Adicella filicornis �Pic������ 1834� B �<br />
*Adicella reducta ��c�ach��a��� 186�� B �<br />
Triaenodes bicolor �C���is�� 1834� B �<br />
Ylodes simulans �Tj�������� 1929� RE B �<br />
Erotesis baltica �c�ach��a��� 1877 CR B<br />
Mystacides azurea ��i��a���s�� 1761� B �<br />
Mystacides longicornis ��i��a���s�� 17�8� B �<br />
Mystacides nigra ��i��a���s�� 17�8� B �<br />
Athripsodes albifrons ��i��a���s�� 17�8� B �<br />
Athripsodes aterrimus �����ph���s�� 1836� B �<br />
Athripsodes bilineatus ��i��a���s�� 17�8� B �<br />
Athripsodes cinereus �C���is�� 1834� B �<br />
Athripsodes commutatus �R�s��c��� 1874� B �<br />
Athripsodes leucophaeus �Ra������ 1842� CR B �<br />
Ceraclea albimacula �Ra������ 1842�<br />
�i�c��. C. alboguttata �Ha������ 1860��<br />
B �<br />
Ceraclea annulicornis �����ph���s�� 1836� B �<br />
Ceraclea dissimilis �����ph���s�� 1836� B �<br />
Ceraclea fulva �Ra������ 1842� EN B �<br />
Ceraclea nigronervosa �R�����i�s�� 1783� EN B �� Ceraclea riparia �����a��a�� 1874� RE B<br />
Ceraclea senilis �B�����is������ 1839� EN B �<br />
Setodes punctatus �Fa��ici�s�� 1793� RE B �<br />
Setodes viridis �F���c��y�� 178�� RE B<br />
Leptocerus interruptus �Fa��ici�s�� 177�� CR B �<br />
Leptocerus tineiformis C���is�� 1834 B �<br />
Oecetis furva �Ra������ 1842� B �<br />
Oecetis lacustris �Pic������ 1834� B �<br />
Oecetis notata �Ra������ 1842� B �2 Oecetis ochracea �C���is�� 182�� B �<br />
<strong>Ferrantia</strong> • 55 / 2008
P. Chvojka, P. Komzák The history and present state of <strong>Trichoptera</strong> research in the Czech Republic<br />
Threat category Czech Republic<br />
Oecetis struckii K��ap������ 1903 CR B �<br />
Oecetis testacea �C���is�� 1834� EN B<br />
*Oecetis tripunctata �Fa��ici�s�� 1793� CR B �<br />
Explanatory notes:<br />
B - B�h���ia�� � - ���avia �i�c����i�� s���h���� pa��<br />
of Silesia); threat categories: RE - regionally extinct,<br />
CR - c�i�ica����y ����a���������� EN - ����a���������� VU<br />
- v�������a����� sp��ci��s.<br />
** - N��w sp��ci��s f�� �h�� fa��a �f �h�� C����ch<br />
Republic:<br />
Rhyacophila laevis Pic������ 1834. B�h���ia ����.��<br />
V�����á �iva E�E ������a �7048-49��� 7�0 � a.s.��.�� ��i�h�<br />
��ap�� 22.-24.vi.2004�� 1 ♂�� J. Ja��š ��� K. �pi������ �����.��<br />
K. N�vá� ����.�� c�����. Na�i��a�� ��s������ P�a����.<br />
Hydroptila vichtaspa �ch�i��� 19�9. ���avia ����.��<br />
the Kazivec brook SW Horní Němčí (48°54‘19‘‘ N,<br />
17°36‘41‘‘ E) (7071), 466 m a.s.l., 1.vii.2005, 91 ♂ 86<br />
♀�� P. Chv�j�a �����. ��� ����.�� c�����. Na�i��a�� ��s������<br />
P�a����.<br />
+ Ceraclea ramburi ���s���� 197�. This sp��ci��s is<br />
��� i�c������� i� �h�� ���a�� ��������� a���h���h ����<br />
�a���� ��a�������� „B�h���ia�� �����a��� 26.�.�� K������a�i“<br />
is ���p�si���� i� Na���his���ich��s ��s���� Wi���<br />
��a��ic�y 200��. � sp��ci���� wi�h s�ch a ��a�����<br />
was �����i����� �y K������a�i �18�9� ������ Ceraclea<br />
nervosa C�q��������.<br />
* - Species for the first time recorded from<br />
Moravia:<br />
Hydropsyche exocellata D�f����� 1841. ���avia<br />
mer.: the Morava river 800 m SE Spytihněv (6871),<br />
7.i�.200��� 1 ♂ p�pa; 12.vi.2006�� 2 ♂; �h�� ���ava<br />
�iv��� �E H����í� �7168��� 12.vi.2006�� 4 ♂; a���� P.<br />
K����á� �����.�� ����. ��� c�����.<br />
Hydropsyche fulvipes �C���is�� 1834�. ���avia<br />
���.�� Š��a�������� ���a�ica�� �a����� �6474��� ��i�h�<br />
��ap�� viii.2001�� 1 ♂�� P. Pav��í� �����.�� P. K����á� ����. ���<br />
c�����.; ���avia ��.�� �i�h� ��i���a�y �f �h�� Záp��ch�vá<br />
s����a� NE N���aš�va �h��a �6874��� 10.vi.200��� 2<br />
♂�� P. Chv�j�a �����. ��� ����.�� c�����. Na�i��a�� ��s������<br />
P�a����.<br />
Agrypnia varia (Fabricius, 1793). Moravia mer.:<br />
Tas�v �7070��� a� ��i�h��� 27.vii.200��� 1 ♂�� P. Chv�j�a<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
�����. ��� ����.�� c�����. Na�i��a�� ��s������ P�a����;<br />
H�a�ic�� �7161��� ��i�h� ��ap�� 30.vii.2004�� 1 ♂�� J.<br />
Š��pich �����.�� P. K����á� ����. ��� c�����.<br />
Adicella reducta ��c�ach��a��� 186��. ���avia ���.��<br />
the Huntava stream 700 m NW Valšovský Důl<br />
(49°50‘34‘‘ N, 17°12‘34‘‘ E) (6169), 15.iv.2003, 1<br />
��a�va�� K. B�a���c �����.�� P. K����á� ����.�� c�����. �asa�y�<br />
U�iv���si�y�� B���.<br />
Oecetis tripunctata �Fa��ici�s�� 1793� - ���avia<br />
����.�� �a��������p���’s ������� D����av�a 4 ��<br />
S Lanžhot (7367), light trap: 24.vii.2004, 1 ♂;<br />
31.vii.2004�� 1 ♂; 3.viii.2004�� 1 ♂; a���� J. Š��pich �����.��<br />
P. K����á� ����. ��� c�����.<br />
R��c������y p����ish��� ���c���s �a��i�i��s �� Chv�j�a<br />
& Novák 2001):<br />
1 - ������á� 2001�� 2 - K����á� & Chv�j�a 200��� 3 -<br />
Němcová 2001, 4 - Komzák, Kroča & Bojková 2006,<br />
� - K����á� 2001<br />
Acknowledgements<br />
W�� a��� ��a���f��� �� Ka����� N�vá��� P���� Pav��í� a��<br />
Ja� Š��pich f�� p��vi�i�� �h�� i�������s�i�� �a����ia��<br />
f��� ��i�h� ��aps. W�� �ha�� a���y���s ���vi��w���<br />
f�� �h�� ���visi�� �f �h�� E����ish �����. Pav���� Chv�j�a<br />
was s�pp������ �y �h�� �i�is��y �f C�������� �f �h��<br />
C����ch R��p����ic �p��j��c� N�. �K00002327201�.<br />
References<br />
Chv�j�a P. 1996. - N��w fa��is�ic ���c���s �f<br />
T�ich�p����a �I�s��c�a� f��� �h�� C����ch R��p����ic.<br />
Časopis Národního muzea, Řada přírodovědná<br />
165: 131-132.<br />
Chv�j�a P. & N�vá� K. 2001. - ���i�i��s a��<br />
c�����c�i��s �� �h�� ch��c���is� �f T�ich�p����a<br />
�I�s��c�a� f��� �h�� C����ch a�� ����va� R��p����ics.<br />
19
P. Chvojka, P. Komzák The history and present state of <strong>Trichoptera</strong> research in the Czech Republic<br />
20<br />
�c�a ��s��i Na�i��a��is P�a�a���� ����i��s B�� His���ia<br />
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K��ap���� F. 1891. - Fi�s� a��i�i��s �� �h�� ch��c���is�<br />
of Czech <strong>Trichoptera</strong> for the year 1890. Věstník<br />
královské české Společnosti Náuk, třída mathematicko-přírodovědecká<br />
1890(2): 176-196. (in<br />
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K��ap���� F. 1894. - ���i�i��s �� �h�� ch��c���is� �f<br />
C����ch T�ich�p����a f�� �h�� y��a�s 1892 a�� 1893.<br />
Věstník královské české Společnosti Náuk,<br />
třída mathematicko-přírodovědecká 1894(2):<br />
1-8. �i� C����ch�<br />
Klapálek F. 1895. - Pelzflügler und Netzflügler<br />
(<strong>Trichoptera</strong> et Neuroptera): 35 p., in Verzeich�is<br />
���� I�s������� Böh����s IV. Ca�a�����s<br />
insectorum faunae bohemicae. Společnost<br />
pro fysiokracii v Čechách, Praha. (in Czech/in<br />
G����a��<br />
K��ap���� F. 1897. - ���i�i��s �� �h�� ch��c���is� �f<br />
C����ch T�ich�p����a f�� �h�� y��a�s 1894-1897.<br />
Věstník královské české Společnosti Náuk,<br />
třída mathematicko-přírodovědecká 1897(62):<br />
1-9. �i� C����ch�<br />
K��ap���� F. 1901. - � c����i���i�� �� �h�� ���w��������<br />
�f �h�� N�����p�����i� fa��a �f �h�� B�h���ia�-<br />
Moravian Uplands. - Věstník České Akademie<br />
Císaře Františka Josefa 10: 489-494. (in Czech)<br />
K��ap���� F. 1903. - � ���p��� �f �h�� s��v��y �f �h��<br />
Czech Neuropteroid fauna in 1902. - Věstník<br />
České Akademie Císaře Františka Josefa 12:<br />
2�7-264. �i� C����ch�<br />
K������a�i F. �. 1848. - G������a ��� sp��ci��s T�ich�p���-<br />
����� I. H�������pa��p�i���a. ��a���i Haas�� Fi����.��<br />
P�a�a���� 108 p.<br />
K������a�i F. �. 18�8a. - B��i���� ��� O��s�������ichs<br />
N�����p�����-Fa��a. Wi������ E���������isch��<br />
Monatschrift 2: 37-49.<br />
K������a�i F. �. 18�8�. - B��i���� ���� K������iss ����<br />
N�����p����a a�s��iaca. Wi������ E���������isch��<br />
Monatschrift 2: 254-256.<br />
K������a�i F. �. 18�9a. - Fa��a ���s ����va����s<br />
(hohen Gesenkes der Sudeten). Jahresheft der<br />
naturwissenschaftlichen Section der k. k. mähr.<br />
schles. Gessellschaft für Ackerbau, Natur- und<br />
Landeskunde, für das Jahr 1858: 1-83.<br />
K������a�i F. �. 18�9�. - G������a ��� sp��ci��s T�ich�p���-<br />
����� II. ���q�ipa��pi�a��. N��v��a�� ����i���s<br />
��� ��a ��ci��� I�p��ia���� ���s Na���a��is���s ���<br />
Moscou 11: 137-300.<br />
K������a�i F. �. 1860. - Ei�i��� ������ I�s������� -<br />
������ v�� ����va���� ����� h�h��� G��s������ ����<br />
����������. Wi������ E���������isch�� ���a�schrift<br />
4: 381-390.<br />
K����á� P. 2001. - Th�� spa�i�-����p��a�� �iv���si�y<br />
in caddisfly communities (<strong>Trichoptera</strong>, Insecta)<br />
�f �h�� Os��ava a�� Chv�j�ic�� s����a�s �C����ch<br />
R��p����ic�. �c�ip�a Fac����a�is �ci����ia���<br />
Na���a��i�� U�iv���si�a�is �asa�y�ia�a��<br />
Brunensis 27 Supplement, Biology: 63-85.<br />
K����á� P. & Chv�j�a P. 200�. - N��w fa��is�ic<br />
���c���s �f T�ich�p����a �I�s��c�a� f��� �h�� C����ch<br />
Republic, II. Časopis Národního muzea, Řada<br />
přírodovědná 174: 65-66.<br />
Komzák P., Kroča J. & Bojková J. 2006. - Interesting<br />
faunistic records of caddisflies (<strong>Trichoptera</strong>)<br />
f��� �h�� ���avs��s������s�� B��s�y�y �����ai�s<br />
(Czech Republic). Časopis Slezského Zemského<br />
Muzea, Série A, vědy přírodní 55: 73-76. (in<br />
C����ch�<br />
�a��ic�y H. 200�. - Ei� ��������i������s V�������ich�is<br />
der Köcherfliegen (<strong>Trichoptera</strong>) Europas und<br />
���s ����i�����a�����i�����s. �i������ �i�����isch��<br />
Beiträge 37: 533-596.<br />
�ay��� K. 1939. - T�ich�p������� ���� ��h���a��i����<br />
Čechoslovakischen Republik. Entomologické<br />
listy 2: 24-36.<br />
Němcová J. 2001. - Macrozoobenthos of the Jihlava<br />
Riv��� ��w�s����a� �h�� Da����šic��-��h������<br />
<strong>Ferrantia</strong> • 55 / 2008
P. Chvojka, P. Komzák The history and present state of <strong>Trichoptera</strong> research in the Czech Republic<br />
���s���v�i�s. �c�ip�a Fac����a�is �ci����ia���<br />
Na���a��i�� U�iv���si�a�is �asa�y�ia�a��<br />
Brunensis 27 Supplement, Biology: 99-128.<br />
N�vá� K. & O�� �. 1977. - T�ich�p����a�� i� D��a����a<br />
J. ����.��� Ch��c� ��is� �sch��ch�s���wa�isch�� I�s���-<br />
����fa��a. �c�a fa��is�ica �����������ica ��s��i<br />
Nationalis Pragae, Supplementum 4: 135-141.<br />
Obr S. 1969. - Zur Kenntnis der Köcherfliegen<br />
�T�ich�p����a� ���� Tsch��ch�s���wa���i II. D���<br />
gegenwärtige Stand der Köcherfliegenforsch���<br />
i� �äh����. F���ia Fac����a�is �ci���-<br />
�ia��� Na���a��i�� U�iv���si�a�is P���y�ia�a��<br />
Brunensis 10(8), Biologia 25: 77-91.<br />
Šá�a�� J. 1920. - Fa��a �f �h�� D��p�vs�� h��y<br />
Mts. <strong>Trichoptera</strong>. - Časopis musea království<br />
českého, oddíl přírodovědný 94: 100-101. (in<br />
C����ch�<br />
������á� E. 1999. - T�ich�p����a�� i� Op�avi���vá V.��<br />
Vaňhara J. & Sukop I. (eds), Aquatic inver-<br />
�����a���s �f �h�� P�ava Bi�sph����� R��s���v��<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
�f UNE�CO. F���ia Fac����a�is �ci����ia���<br />
Na���a��i�� U�iv���si�a�is �asa�y�ia�a��<br />
Brunensis, Biologia 101: 201-206.<br />
������á� E. 2001. - T�ich�p����a f��� c����a�� a��<br />
��pi�hi�h�a�� �f �h�� ���avic�� i� V�����á K����i�a<br />
Ci�q��� a�� ��h��� si���s �f �h�� J��s���í�y<br />
�����ai�s. �c�ip�a Fac����a�is �ci����ia���<br />
Na���a��i�� U�iv���si�a�is �asa�y�ia�a��<br />
Brunensis 27 Supplement, Biology: 159-171.<br />
Stein J. P. E. F. 1873. - Ein Ausflug nach dem<br />
����va����-G���i����. E���������isch�� Z��i������<br />
Stettin 34: 233-243.<br />
����i� J. P. E. F. 1874. - B��i��a� ���� K������iss ����<br />
Ph�y�a���i���� ���s ����va����s ��� ��i�i����<br />
anderer. Entomologische Zeitung, Stettin 35:<br />
244-2�3.<br />
Sukop I. 1990. - Influence of the water works at<br />
N�v� ���ý�y �� �ac�����������h�s �f �h�� Dyj��<br />
Riv��� i� �h�� vici�i�y �f �i�sph����� ���s���v�� P�ava<br />
(southern Moravia). Ekológia (ČSSR) 9: 73-86.<br />
21
F. Cianficconi, C. Corallini, B. Todini The genus Rhyacophila Pictet, 1834 in Italy<br />
22<br />
The genus Rhyacophila Pictet, 1834 in Italy<br />
Abstract<br />
Th�� ��is� �f I�a��ia� Rhyacophila sp��ci��s has ������ �p�a����<br />
�� 200� �ha��s �� �h�� sp��ci����s ca��h� i� I�a��ia� ����i��<br />
waters after the year 2000.<br />
The list includes 35 species and 4 subspecies: 1 of them is<br />
���w �� sci���c�� �Rhyacophila dorsalis pantinii Va�������� 2001�; 3<br />
�f �h��� a��� ���w �� �h�� I�a��ia� fa��a �Rhyacophila polonica<br />
�c�ach��a��� 1879; R. schmidinarica U��a�ic�� K��s�i� &<br />
�a��ic�y�� 2000; R. dorsalis persimilis �c�ach��a��� 1879�<br />
and 8 are recorded for the first time in several Italian<br />
R���i��s.<br />
Th�� ������� �f sp��ci��s i� �h�� P���i�s���a ���c���as��s f���<br />
����h �� s���h. 8 sp��ci��s �f c�����a��-E���p��a� ��i�i� a���<br />
f���� ����y i� �h�� ���ps a�� ��� a����� �h�� �p����i���s.<br />
Résumé<br />
�a ��is��� ���s ��spèc��s i�a��i������s ��� Rhyacophila a ��� �is��<br />
a j��� j�sq��a 200� ��ac�� a�� ������p��ai���s cap����s �a�s<br />
����s ��a�� c���a����s ��I�a��i�� ���p�is ���a����� 2000.<br />
�a ��is��� c��p����� 13 ��spèc��s ��� 4 s��s-��spèc��s pa��i<br />
����q���������s 1 ��s� ���v�������� p��� ��a sci���c�� �Rhyacophila<br />
dorsalis pantinii Va�������� 2001��� 3 s��� ���v��������s p��� ��a<br />
fa���� i�a��i������ �Rhyacophila polonica �c�ach��a��� 1879;<br />
R. schmidinarica U��a�ic�� K��s�i� & �a��ic�y�� 2000 ;<br />
R. dorsalis persimilis �c�ach��a��� 1879� ��� 8 ��� ���<br />
�����i������s p��� ��a p����i�� f�is i� p���si������s ����i��s<br />
i�a��i������s.<br />
��� ������� ���s ��spèc��s �i�i���� �a�s ��a P���i�s����� ��<br />
���� a� s��. 8 ��spèc��s ����i�i��� c�������-�����p�������� ���<br />
��� ����v���s s������������ �a�s ����s ���p��s ��� ��� pas �a�s<br />
Fernanda Cianficconi<br />
Carla Corallini<br />
Barbara Todini<br />
Dipa��i������ �i Bi�����ia C���������a��� �� ���i����a����<br />
�����i���� �i Bi�����ia ��i�a���� ��� Ec�����ia<br />
Università di Perugia, Via Elce di Sotto<br />
I-06123 P�����ia<br />
f����a��a@��ip�.i�<br />
���si�a��@��ip�.i�<br />
fa����i�i@��i�����.i�<br />
Th�� ��s� wi���sp���a� sp��ci��s i� �h�� I�a��ia� R���i��s a���<br />
Rhyacophila simulatrix �c�ach��a��� 1879 a�� R. tristis<br />
Pic������ 1834. 8 sp��ci��s a�� 3 s��sp��ci��s a��� �������ic ��<br />
I�a��y a�� �h��i� p���c����a��� i�c���as��s i� �h�� P���i�s���a<br />
f��� ����h �� s���h.<br />
F��� ha�i�s �f ��a�va�� a�� �h�� p���s���c�� �f sy��i���s a���<br />
i�v��s�i�a����. �� �h�� ��as� i�s�a� �h�� ��a�va�� a��� ca��iv����s.<br />
Th�� sy��i���s�� N���a�����pha�� G����a�i�i�a a��<br />
�ca�i�a a��� ��s���v���. Cys�s �f N���a�����pha a��� �h��<br />
��s� wi�����y �is��i������. I� �h�� �i���s�iv�� ��ac� �f �h��<br />
��a�va���� �h����� sp��ci��s �f �����a�i��� �f �����s Asterophora<br />
a��� p���s����. O���y ���� a����� �f Rhyacophila intermedia was<br />
pa�asi�i����� �y ��a�va�� �f Hy��aca�i�a.<br />
����s �pp����i���s. ���s ��spèc��s ����s p���s ���pa�����s �a�s ����s<br />
����i��s i�a��i������s s��� Rhyacophila simulatrix �c�ach��a���<br />
1879 a�� R. tristis Pic������ 1834. 8 ��spèc��s ��� 3 s��s��spèc��s<br />
s��� �������iq���s p��� ���I�a��i�� ��� ������ p���c����a���<br />
a��������� �a�s ��a P���i�s����� �� ���� a� s��.<br />
��� ����i��� a��i�����ai��� ���s ��a�v��s ai�si q��� ������s<br />
sy��i�����s ��� ��� �����i�s. ���s ��a�v��s ��� �����i���<br />
s�a��� s��� ca��iv����s. O� a ��s���v� ����s sy��i�����s<br />
N���a�����pha�� G����a�i�i�a ��� �ca�i�a. ���s �ys���s ���<br />
N���a�����pha s��� ����s p���s ���pa���s. Da�s ���� �����<br />
�i���s�iv�� ���s ��a�v��s 3 ��spèc��s ��� �����a�i��� �� �������<br />
Asterophora ��� ��� �������v���s. U� s����� a������� ��� Rhyacophila<br />
intermedia a ��� pa�asi�� pa� ��a ��a�v��s ��� Hy��aca�i�a.<br />
<strong>Ferrantia</strong> • 55 / 2008
F. Cianficconi, C. Corallini, B. Todini The genus Rhyacophila Pictet, 1834 in Italy<br />
Zusammenfassung<br />
Die Liste der Italienischen Arten der Gattung Rhyacophila<br />
is� �is 200� ���� �������a����i���� w�������� �a�� ���� �ach<br />
���� Jah� 2000 i� ���� i�a��i���isch��� F��i��ß���wäss����<br />
���f��������� E����p��a����.<br />
Di�� �is��� ��fass� 3� ������ ��� 4 U�����a����� ��i�. Ei��� ���<br />
ist für die Wissenschaft neu (Rhyacophila dorsalis pantinii<br />
Va�������� 2001��� 3 ������ si�� fü� �i�� I�a��i���isch�� Fa��a ����<br />
�Rhyacophila polonica �c�ach��a��� 1879; R. schmidinarica<br />
U��a�ic�� K��s�i� & �a��ic�y�� 2000; R. dorsalis persimilis<br />
�c�ach��a��� 1879��� ��� 8 ������ si�� ���� ���s���� �a��<br />
i� vi������� i�a��i���isch��� R���i����� ���i���� w������. Di��<br />
��������ah�� v����i������ sich v�� N������ i� Rich����<br />
�ü���� .<br />
8 Arten mitteleuropäischen Ursprungs wurden nur<br />
i� ���� ���p����� a���� �ich� i� �pp����i� ���f������. Di��<br />
Introduction<br />
Th�� fa�i��y Rhyac�phi��i�a�� is ���� �f �h�� ��s�<br />
wi���sp���a� �f �h�� T�ich�p����a i� ����i�� wa����s i�<br />
I�a��y. I� �h�� �hi�� ��is� �f I�a��ia� T�ich�p����a �p�a����<br />
to the year 2000 (Cianficconi 2002), 35 species and<br />
2 s��sp��ci��s �f Rhyacophila �����s w����� ��is����.<br />
This ����iv��� f��� ���s��a�ch ca��i��� ��� �v��� �a�y<br />
y��a�s �1884-2000� i� sa�p��i�� si���s ���ca���� i� �h��<br />
Alps (McLachlan 1884; Moretti 1937; Cianficconi<br />
& Moretti 1985a, 1987, 1992; Cianficconi, Corallini<br />
& Moretti 1999), Prealps (Cianficconi, Moretti &<br />
Valle 1993), Apennines (Campadelli, Cianficconi<br />
& Moretti 1990; Cianficconi, Corallini, Moretti &<br />
Salerno 1994; Cianficconi, Moretti & Papagno 1991;<br />
Cianficconi, Moretti & Tucciarelli 1986) and in the<br />
islands Sicilia (Cianficconi, De Pietro, Gerecke &<br />
Moretti 1999), Sardegna (Moretti & Cianficconi<br />
1983; Cianficconi, Corallini, Moretti & Azara 1996),<br />
Elba (Moretti, Gianotti, Taticchi & Viganò 1981).<br />
Th�� ai� �f �his w��� is �� �p�a��� �h�� Rhyacophila ��is�<br />
with findings by Malicky (2002, 2004, 2005, in litt.<br />
2002� a�� �y Va������ �2001� a����� �h�� P���i�s���a�� as<br />
w������ as �� a�a��ys�� �h�� p���s���� �is��i���i�� a�� �h��<br />
��c�����ica�� a�� ch�������ica�� asp��c�s. I� I� a��i�i���� a��i�i����<br />
sy��i���s a�� pa�asi���s �f s���� sp��ci��s hav��<br />
also been observed (Moretti & Sorcetti Corallini<br />
1976; Moretti & Corallini Sorcetti 1981; Corallini<br />
Sorcetti 1984, Cianficconi et al. 1993; Cianficconi et<br />
al. 1995; Moretti et al. 1997; Cianficconi et al. 1998;<br />
Cianficconi et al. 1999�.<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
v�������i���s���� ������ i� ���� i�a��i���isch��� R���i����� si��<br />
Rhyacophila simulatrix �c�ach��a��� 1879 ��� R. tristis<br />
Pic������ 1834. 8 ������ ��� 3 U�����a����� si�� �������isch i�<br />
I�a��i����� ih� B��s�a�� ���höh� sich v�� N��� �ach �ü� ����<br />
Ha���i�s����. �a� ha� �i�� E��äh����s���w�h�h��i���� ����<br />
�a�v��� ��� �i�� ��w��s���h��i� v�� �y��i������ ������s�ch�.<br />
Di�� �a�v��� ���s ����������� ��a�i��s si�� �a��iv��. �a�<br />
ha� �i�� �y��i������ N���a�����pha, G����a�i�i�a ���<br />
�ca�i�a �����ach����. Di�� Zys���� v�� N���a�����pha<br />
sind die häufigsten. In dem Verdauungstrakt von<br />
�a�v��� si�� 3 ������ ���� G����a�i�i�a a�s ���� G����s<br />
Asterophora ���f������ w������. N�� ��i� a�������s E����p��a�<br />
v�� Rhyacophila intermedia w����� v�� �a�v��� ����<br />
Hy��aca�i�a pa�asi�i����.<br />
Material and methods<br />
Th�� Rhyacophila w����� sa�p����� as ��a�va���� p�pa��<br />
a�� a�����s�� i� ����� �ha� 1�00 sa�p��i�� si���s �y<br />
���s��a�ch���s a�� ��������a��a��� s�������s �f �h��<br />
Is�i���� �i Z������ia�� U�iv���si�à �i P�����ia. Th��<br />
a�����s w����� c�������c���� i� �ay��i�h� a�� s�����i���s<br />
���i�� �h�� �i�h� wi�h ��i�h� ��aps. ����� ��a�va�� w�����<br />
���a���� i� cap�ivi�y i� ������ �� s���y �h�� �i�����ica��<br />
cyc����s �f �h�� ���sp��c�iv�� sp��ci��s.<br />
F�� �h�� sy��i��� s���y�� �h�� ��a�va�� w����� �iss��c����.<br />
For light microscopy the gut was fixed in formol<br />
4 %. F�� sca��i�� a�� ��as�issi�� ������c����<br />
microscopy the gut was fixed in Karnovsky<br />
medium in cacodylate buffer (pH 7.2).<br />
Observations and discussion<br />
Ecological remarks<br />
Th�� aq�a�ic i�s�a�s i�ha�i� ����ic �i�������s f���<br />
crenal (Cianficconi, Corallini & Moretti 1998) to<br />
ip��i�h�a���� p���f���a���y ��pi�i�h�a���� wi�h a s��s��a���<br />
�f ��av���� a�� s�����s �Fi�. 1�. ����� sp��ci��s ���.�.<br />
R. pubescens�� R. tristis) often live in hygropetric<br />
ha�i�a�s�� c�v������ wi�h ��ss��s �Fontinalis<br />
antipyretica, Fissidens crassipes, Cratoneuron<br />
filicinum) (Cianficconi et alii 200��.<br />
23
F. Cianficconi, C. Corallini, B. Todini The genus Rhyacophila Pictet, 1834 in Italy<br />
24<br />
Fig. 1: Preferred habitat of Rhyacophila aquatic instars.<br />
The biozones are located at different altitudes<br />
�f��� 1 �� 2600 � a.s.��.� a�� �h�� hi�h��s� ������� �f<br />
sp��ci��s was f���� a� ����i�� a�� hi�h a���i�����s.<br />
The most significant physico-chemical parameters<br />
are: clear, cool waters, concentration of O 2 �s�a����y<br />
near saturation point, various flow rates, various<br />
����v����s �f ha�����ss �f��� �-7 F����ch ���������s ��<br />
��a�i�ic s��s��a��� i� �h�� w��s����� ���ps�� Ca��a��ia a��<br />
�a������a �� 10-30 F�. ���. �� ca��ca�����s s��s��a����<br />
a�� �f pH �f��� �.�-6.� �� ��a�i�ic s��s��a��� �� 7-8<br />
�� ca��ca�����s s��s��a����.<br />
O���y �h�� ��a�va�� �f R. dorsalis acutidens s����� ��<br />
a�ap� �� s��i�h���y p���������� wa����s �as i� Ti���� �iv����<br />
(Moretti & Cianficconi, 1984).<br />
� f��w sp��ci��s ���.�. R. vulgaris, R. intermedia, R.<br />
rougemonti� a��� �ccasi��a����y f���� as a�����s i�<br />
caves (Moretti & Gianotti 1967; Cianficconi &<br />
Moretti, 1985).<br />
List and distribution updated to 2005<br />
I� Ta����� 1 �h�� sp��ci��s f���� i� �h�� 18 I�a��ia� ����i��s<br />
a�� 3 is��a��s a��� ��is���� as i� �h�� ch��c���is� �f I�a��ia�<br />
<strong>Trichoptera</strong> (Moretti & Cianficconi 1995) and their<br />
ch����yp��s a��� sh�w�.<br />
T� �a��� 3� sp��ci��s a�� 4 s��sp��ci��s hav�� ������<br />
f����. C��pa���� �� �h�� p���vi��s ��is��� 2 sp��ci��s a���<br />
new findings: R. polonica f���� i� F�i���i V�������ia<br />
Gi���ia ��a��ic�y 200�� a�� R. schmidinarica f����<br />
i� T�����i�� ����� ��i��� ��a��ic�y in litt. 2002�. 2 �a�a<br />
hav�� a ���w s�a��s ���ca�s�� R. dorsalis �C���is�� 1834�<br />
was ��a�sf������� �� s��sp��ci��s R. dorsalis persimilis<br />
��a��ic�y�� 2002� a�� R. nubila (Zetterstedt, 1840)<br />
�� �h�� ���c������y ���sc�i���� s��sp��ci��s R. dorsalis<br />
pantinii �Va�������� 2001�.<br />
Ei�h� sp��ci��s ����������� �h��i� �is��i���i�� i� �h��<br />
P���i�s���a. ����� �h��s�� R. dorsalis acutidens<br />
����������� f��� c�����a�� s���h���� �p����i���s ��<br />
����h-w��s����� I�a��y ��a��ic�y 2002��� R. orobica f���<br />
����a��ia �� T�����i�� ����� ��i��� a�� V�������<br />
��a��ic�y 200�� a�� R. vallei f��� Ca��a��ia ��<br />
����is���� Ca�pa�ia a�� Basi��ica�a �Va������ 2001�.<br />
The list shows a significant difference between the<br />
���ps�� �h�� �p����i���s a�� �h�� Is��a��s. I� �h�� c�����a��<br />
���ps �h�� hi�h��s� ������� �f sp��ci��s was f���� i�<br />
����a��ia a�� T�����i�� ����� ��i��� �19��� i� �h��<br />
c�����a�� �p����i���s i� T�sca�a �12�� i�c����i�� �h��<br />
�p�a�ia� ���ps� a�� i� �h�� s���h���� �p����i���s i�<br />
Ca��a��ia �9�. 2 sp��ci��s w����� f���� i� �ici��ia�� 2 i�<br />
�a������a a�� 1 s��sp��ci��s i� E���a.<br />
<strong>Ferrantia</strong> • 55 / 2008
F. Cianficconi, C. Corallini, B. Todini The genus Rhyacophila Pictet, 1834 in Italy<br />
Tab. 1: List and distribution of italian Rhyacophila updated to 2005:<br />
= taxa included in the third list;<br />
TAXA<br />
Rhyacophilidae<br />
Th�� ��s� wi���sp���a� sp��ci��s a��� R. simulatrix<br />
�16 R���i��s� a�� R. tristis �1���� �h�� �a���s� a��� R.<br />
palmeni, R. polonica, R. schmidinarica f���� ����y i�<br />
���� R���i��.<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
REGIONS AND ISLANDS<br />
= new finding in Italy (Malicky); = new to science (Valle); = new finding in the Region<br />
(Malicky); = new finding in the Region (Valle). Chorotype names: APPE = Apennine endemic; CEU = Central-European; ALSW =<br />
SW-Alpine endemic; APPS = S-Apennine endemic; EUR = European; APPC = Central-Apennine endemic; WEU = W-European; SACO =<br />
Sardo-Corsican endemic; EME = E-Mediterranean; AWNA = W-Alpine-N-Apennine endemic. (Vigna Taglianti et a 1999).<br />
Piemonte<br />
Valle d'Aosta<br />
Liguria<br />
Lombardia<br />
Trentino A.Adige<br />
Veneto<br />
Friuli V.Giulia<br />
1 Rhyacophila albardana , McLachlan, 1879 � � � � � � � � � � 11 CEU<br />
2 R. appennina McLachlan, 1898 E � � 2 APPE<br />
3 R. aquitanica McLachlan, 1879 � � � � � 5 CEU<br />
4 R. arcangelina Navas, 1932 E � � 2 ALSW<br />
5 R. aurata Brauer, 1857 � � � � 4 CEU<br />
6 R. bonaparti Schmid, 1947 � � 2 CEU<br />
R. dorsalis acutidens McLachlan, 1879 E � � � � � � � � � � 12 APPE<br />
R.dorsalis pantinii Valle, 2001 E 2 APPS<br />
R. dorsalis persimilis McLachlan, 1879 0 CEU<br />
7 R. fasciata Hagen, 1859 � � 2 EUR<br />
8 R. foliacea Moretti, 1981 E � � � � � � � � � 9 APPC<br />
9 R. glareosa McLachlan, 1867 � � � � 4 CEU<br />
10 R. hartigi Malicky, 1971 E � � � � 4 APPS<br />
11 R. hirticornis McLachlan, 1879 � � � � 4 EUR<br />
12 R. intermedia McLachlan, 1868 � � � � � � � 8 EUR<br />
13 R. italica Moretti, 1981 E � � � � 4 APPC<br />
R. italica ilvana Moretti, 1981 E � 1<br />
14 R. kelnerae Schmid, 1971 � � � 3 WEU<br />
15 R. laevis Pictet, 1834 � � � � 4 EUR<br />
16 R. meyeri McLachlan, 1879 � � � � � � 6 CEU<br />
17 R. orobica Moretti, 1991 � 3 CEU<br />
18 R. pallida Mosely, 1930 � 1 SACO<br />
19 R. palmeni McLachlan, 1879 � 1 EME<br />
20 R. pascoei McLachlan, 1879 � � � � 4 EUR<br />
21 R. polonica McLachlan , 1879 1 CEU<br />
22 R. praemorsa McLachlan, 1879 � � 4 CEU<br />
23 R. producta McLachlan, 1879 � � � 3 CEU<br />
24 R. pubescens Pictet, 1834 � � � � � � � � � � 10 EUR<br />
25 R. ravizzai Moretti, 1991 E � 2 AWNA<br />
26 R. rectispina McLachlan, 1884 � � � � 4 CEU<br />
27 R. rougemonti McLachlan, 1880 E � � � � � � � � � � 10 APPS<br />
28 R. schmidinarica (Urbanic-Krusnik -Malicky 2000) 1 CEU<br />
29 R. simulatrix McLachlan, 1879 � � � � � � � � � � � � � � � � 16 CEU<br />
30 R. stigmatica (Kolenati, 1859) � � � � � 5 CEU<br />
31 R. torrentium Pictet, 1834 � � � � � � 7 CEU<br />
32 R. trifasciata Mosely, 1930 � 1 SACO<br />
33 R. tristis Pictet, 1834 � � � � � � � � � � � � � � � 15 EUR<br />
34 R. vallei Moretti, 1997 E � 4 APPE<br />
35 R. vulgaris Pictet, 1834 � � � � � � � � � � 10 CEU<br />
Total 18 7 12 18 19 12 15 9 12 8 9 9 8 7 7 2 8 9 2 2 1<br />
Emilia Romagna<br />
Toscana<br />
Umbria<br />
Marche<br />
Lazio<br />
Abruzzo<br />
Molise<br />
Campania<br />
Puglia<br />
Chorological remarks<br />
I� I�a��y�� �h�� �����s Rhyacophila ���p���s����s 31% �f<br />
�h�� sp��ci��s a�� 2� % �f �h�� s��sp��ci��s ���w� i�<br />
E���p�� ��a��ic�y 2004�.<br />
Basilicata<br />
Calabria<br />
Sicilia<br />
Sardegna<br />
Elba<br />
Total<br />
Chorotypes<br />
25
F. Cianficconi, C. Corallini, B. Todini The genus Rhyacophila Pictet, 1834 in Italy<br />
26<br />
Th�� ����������aphica�� �a��a�c�� sh�ws a<br />
p������i�a�c�� �f sp��ci��s wi�h C�����a�� - E���p��a�<br />
�is��i���i�� �41 %��� f������w��� �y �h�s�� wi�h<br />
E���p��a� �18 %� a�� W��s����� ����i�����a���a�<br />
����1 %� �is��i���i��. 8 sp��ci��s a�� 3 s��sp��ci��s<br />
��a����� E i� Ta�. 1� a��� �������ic �� �h�� I�a��ia�<br />
fa��a.<br />
I� is �����w���hy �ha� a���� �h�� sp��ci��s �f<br />
C�����a��- E���p��a� ��i�i��� s���� a��� ��i�i����<br />
�� �h�� I�a��ia� ���ps �R. aquitanica�� R. aurata�� R.<br />
bonaparti�� R. glareosa, R. hirticornis, R. polonica�� R.<br />
Fig. 2: Distribution of 3 vicariant species of Rhyacophila<br />
gr. vulgaris: ● = R. vulgaris; = R. foliacea; � =<br />
R. hartigi<br />
Fig, 3: Distribution of 3 vicariant subspecies of R. dorsalis:<br />
▪ = R. dorsalis persimilis; = R. dorsalis acutidens;<br />
● = R. dorsalis pantinii.<br />
producta�� R. stigmatica��� ��h���s a��� vica�ia���� a�����<br />
�h�� p���i�s���a �y si�i��a� sp��ci��s. R. vulgaris is<br />
vica�ia���� i� �h�� c�����a�� �p����i���s �y R. foliacea<br />
a�� i� �h�� s���h���� �p����i���s a�� �ici��ia �y R.<br />
4<br />
�<br />
Figs. 4, 5: Distribution of Rhyacophila gr. rougemonti in<br />
the W- Mediterranean region.<br />
= R. italica; = R. italica ilvana; = R. rougemonti;<br />
● = R. pallida; = R. trifasciata. R. vallei (�) is similar<br />
to Corsican R. tarda ( ) 5) W- Mediterranean microplates<br />
in the Oligocene (by Alvarez, Cocozza and Wezel<br />
1974).<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
R. dorsalis persimi<br />
R. dorsalis acutide<br />
R. dorsalis pantinii
F. Cianficconi, C. Corallini, B. Todini The genus Rhyacophila Pictet, 1834 in Italy<br />
6<br />
7<br />
18<br />
3<br />
2<br />
12<br />
4<br />
19<br />
hartigi �Fi�. 2�. Th�� s��sp��ci��s R. dorsalis persimilis<br />
is vica�ia���� i� �h�� w��s����� ���ps a�� c�����a��<br />
�p����i���s �y R. dorsalis acutidens a�� i� s���h����<br />
�p����i���s �y R. dorsalis pantinii �Fi�. 3�.<br />
����� �h�� sp��ci��s �f W��s����� ����i�����a���a�<br />
�is��i���i�� �h�� �a���-C��sica� R. pallida a�� R.<br />
trifasciata a��� vica�ia���� i� �h�� s���h���� �p����i���s<br />
a�� �ici��y �y si�i��a� sp��ci��s R. rougemonti a��<br />
i� �h�� c�����a�� �p����i���s �y R. italica. ������v���<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
1<br />
9 2<br />
12<br />
4<br />
19<br />
12<br />
9<br />
8<br />
4<br />
4<br />
9<br />
3<br />
15<br />
8 3<br />
6<br />
7<br />
7<br />
Fig. 6: Total number of species found in each region and<br />
number of Italian endemic species (encircled number).<br />
2<br />
Tab. 2: Species of Rhyacophila examined and their Symbionts.<br />
5<br />
8<br />
4<br />
9<br />
2<br />
5<br />
R. vallei �f �h�� s���h���� �p����i���s is si�i��a� ��<br />
C��sica� R. tarda Gi��ic������i�� 1968. �Fi�. 4�.<br />
These distributions could confirm the hypothesis<br />
�ha� �h�� ��i�i�a�� c�����i��a�i�� �f Rhyacophila i� �h��<br />
P���i�s���a �cc������ �ai���y via �h�� ���ps i� �h��<br />
����h a�� wi�h �h�� ��a�s��a�i�� �f �h�� c���i�����a��<br />
�a���-�ici��ia�-Ca��a��ia� �ic��p��a��� i� �h�� w��s�<br />
(Cianficconi & Moretti 1990) (Fig. 5).<br />
I� is i�������s�i�� �� ����� �ha� i� �h�� ����h���� ����i��s<br />
�Va������ ����s�a�� ����a��ia�� T�����i�� ����� ��i�����<br />
V��������� F�i���i V�������ia Gi���ia� �h����� a��� �� �������ic<br />
sp��ci��s a�� �ha� �h�� p���c����a��� �f �������ic sp��ci��s<br />
i�c���as��s i� �h�� P���i�s���a f��� �h�� ����h w��s� ��<br />
�h�� s���h ��p���ia�� a�� �ici��y 100%�� ����is�� �8�%�<br />
a�� Ca�pa�ia �71%� �Fi�.6�.<br />
Feedings and symbionts<br />
Th�� f�����i�� ����i��� a�� �h�� p���s���c�� �f sy��i���s<br />
a��� i�v��s�i�a���� i� 14 sp��ci��s �f Rhyacophila �Ta�.<br />
2). These belong to 4 subgenera sensu Döhler:<br />
Hyp��hyac�phi��a �R. pubescens�� R. tristis�; Pa�a�hyac�phi��a<br />
�R. intermedia�� R. italica�� R. pallida�� R.<br />
rougemonti�� R. trifasciata�; Hyp����hyac�phi��a �R.<br />
torrentium�; Rhyac�phi��a s s��. ��R. dorsalis acutidens��<br />
R. dorsalis persimilis�� R. foliacea�� R. hartigi�� R.<br />
simulatrix�� R. vulgaris �.<br />
Gregarinida Nematomorpha Hydracarina<br />
R. dorsalis acutidens Asterophora mucronata Lèger, 1892 Gordius sp. (cyst)<br />
R. dorsalis persimilis Asterophora mucronata Lèger, 1892 Gordius sp. (cyst)<br />
R. foliacea Asterophora mucronata Lèger 1892 Gordius sp. (cyst)<br />
R. hartigi Asterophora heerii Kőlliker, 1848 Gordius sp. (cyst)<br />
R. intermedia larvae<br />
R. italica Asterophora mucronata Lèger, 1892<br />
R. pallida Asterophora heerii Kőlliker, 1848 Gordius sp. (cyst)<br />
R. pubescens Asterophora mucronata Lèger, 1892 Gordius sp. (cyst)<br />
R. rougemonti Asterophora mucronata Lèger, 1892 Gordius sp. (cyst)<br />
R. simulatrix Asterophora mucronata Lèger, 1892 Gordius sp. (cyst)<br />
R. torrentium Asterophora capitata Boudoin, 1967 Gordius sp. (cyst)<br />
R. trifasciata Asterophora heerii Kőlliker, 1848 Gordius sp. (cyst)<br />
R. tristis Asterophora mucronata Lèger, 1892 Gordius sp. (cyst)<br />
Asterophora mucronata Lèger, 1892<br />
R. vulgaris Asterophora heerii Kőlliker, 1848 Gordius sp. (cyst)<br />
Asterophora mucronata Lèger, 1892<br />
27
F. Cianficconi, C. Corallini, B. Todini The genus Rhyacophila Pictet, 1834 in Italy<br />
28<br />
d<br />
a<br />
b<br />
e<br />
c<br />
Fig. 7: a) Gut content of the Rhyacophila larva b) Astherophora mucronata: Trophozoite c)<br />
A. mucronata: Transverse section, trophozoite showing epicyte folds (TEM bar =1 µm) d) A.<br />
mucronata: Gamont, surface arranged in longitudinal epycite folds (SEM bar =10 µm) e) A.<br />
mucronata: Longitudinal section, nucleus of gamont including bacteria (TEM bar = 0,5 µm).<br />
<strong>Ferrantia</strong> • 55 / 2008
F. Cianficconi, C. Corallini, B. Todini The genus Rhyacophila Pictet, 1834 in Italy<br />
a<br />
Fig. 8: Nematomorpha immature stages are internal parasites of Rhyacophila larvae, pupae and<br />
adults: a) Several cysts in muscular layers of the midgut wall b) Cyst of Nematomorpha larva (bar<br />
= 35 µm).<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
b<br />
29
F. Cianficconi, C. Corallini, B. Todini The genus Rhyacophila Pictet, 1834 in Italy<br />
30<br />
a b<br />
Fig. 9: Hydracarina indet. (suborder Trombidiformes) ectoparasite on Rhyacophila adults:<br />
a) Hydracarina larva b) Gnatosoma. Inset: detailed drawing.<br />
Th�� ��a�va�� a� �h�� ��as� i�s�a�s a��� �ypica����y<br />
ca��iv����s p����a���s�� which f����� a��v�� a����<br />
�� ��a�va�� �f ��h��� aq�a�ic i�s��c�s�� i�c����i��<br />
T�ich�p����a. ���v���a�� f�a������s �f c��ic���� hav��<br />
������ ��s���v��� �Fi�. 7a�.<br />
The digestive tract consists of three regions:<br />
f��������� �i���� a�� hi�����. Th�� f������� �f<br />
�h�� ��a�va�� is pa��ic���a���y ����� a�� has c��ic���a�<br />
s���c�����s�� �ai���y spi���s which cha�ac����is�ica����y<br />
point towards the buccal cavity (Corallini Sorcetti<br />
& Catapano 1988; Spinelli Batta & Corallini<br />
Sorcetti, 1988).<br />
Th�� p���s���c�� �f sy��i���s is f���q�������y<br />
��s���v���.<br />
R��vi��wi�� �h�� P�������a E������a�i�i�a p���s����<br />
i� �h�� �i���� �f Rhyacophila�� �h����� sp��ci��s �f �h��<br />
�����s Asterophora w����� ��s���v���. A. mucronata is<br />
�h�� ��s� wi���sp���a��� i� s���� cas��s 60-6� % �f<br />
�h�� ��a�va�� w����� i�f��s����. T��ph����i���s �a����s��<br />
sy��y�y a�� �a�����cys�s w����� ��s���v��� �C��a����i�i<br />
1997). The trophozoite is 40 – 100µm long (Fig.<br />
7b), the gamont 80 – 140µm. The gamont surface<br />
is a��a����� i� a� ��picy��� f���� a����� �h�� c������ ���y<br />
�Fi�. 7��. Th�� p������ic���� has �h����� c���ica�� ������a���s��<br />
the epicyte folds have filaments localized to the<br />
�is�a�� �ip �Fi�. 7c�. I� �h�� cy��p��as� �i��ch����ia��<br />
�����p��as�ic ����ic������� f����� �i��s����s�� G����ia�<br />
v��sic����s�� pa�a���yc����� ��a������s �Fi�. 7c� a��<br />
������c���� ����s�� ���i��s. w����� ��s���v���. Th�� �a����<br />
has �ac����ia i�si��� �h�� ��c�����s �Fi�. 7���.<br />
A. capitata is p���s���� ����y i� Va�� ����s�a a�� A.<br />
heeri ����y i� �a��i�ia.<br />
N���a�����pha �f �h�� �����s Gordius�� a��� �h�� ��s�<br />
wi�����y �is��i������ a�� a��� f���� as cys�s i� �h��<br />
��a�va���� p�pa�� a�� a�����s. �Fi�. 8a-��.<br />
After hatching the larva of Gordius i�����ia�����y<br />
p�������a���s a� aq�a�ic a�i�a���� p���f���a���y a� i�s��c�.<br />
Th�� ��a�va c���i����s i�s ���v�����p����� ����y if �h��<br />
h�s� is s�i�a�����.<br />
Th�� ��a�va�� i����s���� �y a� ��s�i�a����� h�s� �i��s<br />
�� ���cys�s i� �h�� �iss���s i�s���a� �f ���v�����pi��<br />
f���h����� as happ���s wh��� �his h�s� is ��a���� �y<br />
a���h��� s�i�a����� i�s��c�.<br />
Rhyacophila is ��� a s�i�a����� h�s� f�� Gordius.<br />
�� a����� �f R. intermedia was pa�asi�i����� �y ��a�va��<br />
of Hydracarina (Fig. 9a-b) attached to the thorax,<br />
a������� a�� �����s.<br />
The Hydracarina larvae, after a short freeswimming<br />
period, become attached to aquatic<br />
i�s��c�s wi�h �h��i� ��a��s��a a�� ass���� a<br />
pa�asi�ic ���is����c��.<br />
Acknowledgements<br />
W�� �ha�� P��f. H. �a��ic�y - ����� �� ������� ��s��ia<br />
- f�� s����i�� �s ��p����ish��� i�f���a�i�� a����<br />
Rhyacophila �f �h�� I�a��ia� ����i��s.<br />
<strong>Ferrantia</strong> • 55 / 2008
F. Cianficconi, C. Corallini, B. Todini The genus Rhyacophila Pictet, 1834 in Italy<br />
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<strong>Ferrantia</strong> • 55 / 2008
A. Dohet et al. Caddisfly assemblages characterizing different ecological areas in Luxembourg<br />
Caddisfly assemblages characterizing different<br />
ecological areas in Luxembourg: from geographical<br />
distributions to bioindication<br />
Abstract<br />
T�a�i�i��a����y�� �h�� G�a�� D�chy �f ����������� is �ivi����<br />
i��� �w� �ai� ��c�����ica�� a���as�� which a��� cha�ac����i�����<br />
by specific geo-morphological and climatic conditions.<br />
Th�� O��s��i�� i� �h�� ����h c�v���i�� ����-�hi�� �f �h��<br />
�����i���y is a h�����������s schis���s H���cy�ia� �assif<br />
wi�h a ���a� a���i����� app��achi�� 4�0 �. Th�� G����a�� i�<br />
�h�� s���h is cha�ac����i����� �y T�iassic a�� J��assic ��ay���s<br />
�� a D��v��ia� �as��. Th�� a���i����� va�i��s ����w����� 2�0<br />
� a�� 400 �. Wi�hi� �h�� G����a���� �w� s��-��c�����i��s<br />
may be further distinguished: the Minette basin and the<br />
��s�������� va������y. Th��s�� ����i��s a��� ���s��ic���� ���sp��c�iv����y<br />
�� �h�� s���hw��s� a�� s���h��as� �f �h�� c�����y.<br />
A database of caddisflies sampled in 239 sites distributed<br />
�v��� �h����� ��� �f �h�� f��� ��c�����ica�� a���as ��� si���s w�����<br />
sa�p����� i� �h�� ��s�������� va������y a���a� is �s��� �� v���ify if<br />
these geographic areas correspond to distinct caddisfly<br />
assemblages. The ability of this landscape classification<br />
to explain variation in caddisflies, was compared to that<br />
�f a �iv��� �yp�����y ��������i���� �� �h�� �asis �f s������c����<br />
a�i��ic va�ia�����s. O��i�a�i�� ����h��s w����� �s��� ��<br />
i�����s��a��� �h�� si��� s��pa�a�i�� acc���i�� �� �i�����ica��<br />
�a�a.<br />
Although there was some overall difference in caddisfly<br />
c��p�si�i�� a���� �h�� �w� �ai� ��c�����ica�� a���as �i.��.<br />
Oesling and Gutland), the different classes were not<br />
w������ s��pa�a���� �� �h�� ���i�a�i�� �ia��a��� i��ica�i�� a<br />
����a� �v�����ap ����w����� sp��ci��s ass������a���s i� �h�� �w�<br />
��c�����ica�� a���as. P�ssi����� ���as��s f�� �h�� �����a�iv�� p���<br />
correlation observed between caddisfly assemblages<br />
Introduction<br />
The classification of streams has a long tradition in<br />
Europe and has always been a matter of strenuous<br />
�isc�ssi��s ����w����� sci����is�s. I� is ��� �h�� ��j��c�iv��<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Alain Dohet, Martial Ferréol<br />
Henry-Michel Cauchie & Lucien Hoffmann<br />
D�pa��������� E�vi����������� ��� ����-�i����ch������i��s �EV��<br />
C������� ��� R��ch���ch�� P����ic Ga��i���� �ipp�a��<br />
41�� ���� �� B�i����<br />
�-4422 B����va��<br />
��h���@��ipp�a��.���<br />
a�� �h�� ������aphic c��ass��s i�c������� ��acc�������-f��<br />
�����i���i�a�� ����a�i�� �f �iv���s a�� ��acc�������-f��<br />
p�������a�i�� ��a�i���� i� �h�� �a�as���. I��������� �h�� �s�� �f<br />
the classification based on the river typology, which can<br />
��� assi�i��a���� �� a pa��i�i�� �f �h��s�� �w� �ai� ��c�����ica��<br />
a���as ���s���� �y �h�� ca�ch������s si���� ��a�i������ a�� �h��<br />
s������c�i�� �f si���s cha�ac����i����� �y ���w a��h��p�����ic<br />
�is����a�c���� i�p��v�� ����a���y �h�� s��pa�a�i�� �f c��ass��s<br />
�� �h�� �����c��� �����i�i����si��a�� spac��. Disc������<br />
clusters indicating distinct caddisfly assemblages are<br />
p���s���� i� �h�� ���i�a�i�� �ia��a�. Th�� i��ica��� va�����<br />
method was then used to identify caddisfly species<br />
characteristic of the different clusters. For instance,<br />
Glossosoma conformis�� Philopotamus ludificatus�� Oecismus<br />
monedula�� Sericostoma personatum/schneideri�� Hydropsyche<br />
instabilis a�� Odontocerum albicorne sh�w hi�h i��ica���<br />
va�����s f�� h��a�wa���� s����a�s i� �h�� O��s��i�� wh���<br />
a��h��p�����ic �is����a�c��s a��� �i�i�a��. Plectrocnemia<br />
conspersa�� Drusus annulatus a�� Potamophylax cingulatus<br />
�� �h�� sa��� f�� h��a�wa���� s����a�s i� �h�� G����a��.<br />
Polycentropus flavomaculatus�� Brachycentrus maculatus��<br />
Mystacides azureus�� Allogamus auricollis�� Silo piceus��<br />
Athripsodes bilineatus a�� Ceraclea annulicornis a��� �h��<br />
���s� i��ica��� sp��ci��s f�� ��a����� a�� ����ss i�pac����<br />
s����a�s i� �h�� O��s��i��. Th�� p��p���i��s a�� i�����i�i��s<br />
�f �h�� T�ich�p����a sp��ci��s�� which a��� cha�ac����is�ic �f �h��<br />
different river types are discussed in relation to humaninduced<br />
alterations that especially affect large lowland<br />
�iv���s i� C�����a�� E���p��.<br />
�f �his pap��� �� �isc�ss �h�� a�va��a���s a��<br />
disadvantages of the different theories (especially<br />
�h�� ����a�i�� sys���� a�� �h�� Riv��� C���i����<br />
C��c��p�� p��p�s��� s� fa�. I�������s�i�� �isc�ssi��s<br />
ca� ��� f���� i� ��������s p����ish��� w���s ���.�.<br />
H���� 1949; I����i��s & B���sa���a�� 1963�� P����a�<br />
33
A. Dohet et al. Caddisfly assemblages characterizing different ecological areas in Luxembourg<br />
34<br />
1971�� V������a�� 1973�� P���s����� 1979�� Va������ et<br />
al. 1980�� W�i�h� et al. 1984�� ��a������� & Hi������ 1986��<br />
B���sa���a�� 1988�� Wass�� 1989�.<br />
Classification of waterbodies is a necessary step for<br />
aq�a�ic �i�����ica�� ass��ss����� a�� is ���c����������<br />
f�� wa���� ���s���c�� a�� c��s���va�i�� �a�a��������.<br />
I��������� �h�� �s�� �f ��c�����i��s as a ������aphic<br />
framework (i.e., �a priori� classifications) on which<br />
�� �as�� ca�ch����� �a�a�������� is ��sp��cia����y<br />
attractive to water quality programs that depend<br />
�� ass��ss�����s �f �����ip���� �i�����ica�� �����������s ��<br />
measure attainment of water quality goals (e.g. fish,<br />
p���iphy����� �ac��phy���s�� �����hic i�v��������a���s ��<br />
phy��p��a������. I��������� �h��s�� �i�����ica�� �����������s<br />
respond to different environmental factors and<br />
the classifications based on communities (i.e.,<br />
�a posteriori� classifications) are not always<br />
c��c���a�� ac��ss �a�����ic ����ps �Paav���a et<br />
al. 2003�. C��s��q�������y�� s�ch a� app��ach w�����<br />
request specific typologies for each taxonomic<br />
����p i�v��s�i�a���� a�� w����� ��� i�app��p�ia��� f��<br />
wa���� �a�a����s. Ec�����i��s a��s� h����p �a�a����s<br />
�� ���v�����p a�� i�p��������� �a�a�������� s��a����i��s<br />
�ha� a�����ss h�w �h�� ca�s��s �f �����a�a�i��<br />
�ay i�����ac� wi�h �h�� ��a��scap���� as w������ as ��<br />
c�����ica��� �h�s�� �����a�i��ships �� �h�� p����ic<br />
�Haw�i�s et al. 2000�.<br />
Ecoregions are classified by mapping<br />
������aphica�� ����i��s wi�hi� which c��i�a������ica��<br />
and landscape attributes, such as topography,<br />
��������y�� a�� ��a�� c�v��� a��� h�����������s a��<br />
�is�i�c�iv�� c��pa���� �� ��h��� ����i��s �����������<br />
et al. 2004�. Th�� ���s����a�� c��ass��s a��� ���p��c���� ��<br />
���p��ai� va�ia�i�� i� ��c�����ica�� cha�ac����is�ics �e.g.<br />
ass������a��� s���c������ a�� �� p����ic��� �� s����<br />
extent, the ecological attributes of those areas<br />
�F���i�������a 2000�. H�w��v����� �h�� s�������h �f �h��<br />
�����a�i��ships ����w����� ��a��scap�� f��a�����s a��<br />
site-specific biota is poorly known (Hawkins et al.<br />
2000�. C��s��q�������y�� a �i�����s ��va���a�i�� �f �h��<br />
�������� �� which �h�s�� a p�i��i ����i��a��i��a�i��s �f<br />
the landscape are able to capture a significant part<br />
�f �h�� �a���a�� va�ia�i�� ass�cia���� �� �h�� �i��a is<br />
���c��ssa�y.<br />
In Europe, the 25 European ecoregions defined by<br />
I����i��s �1978� a��� f���q�������y �s��� as a f�a���w���<br />
f�� �a�i��a�� �yp�����i��s�� pa��ic���a���y f�� app��i���<br />
p��p�s��s ��i��� �h�� i�p���������a�i�� �f �h�� EU Wa����<br />
F�a���w��� Di���c�iv�� �WFD� �EU 2000� ���������<br />
et al. 2004�. Th�� G�a�� D�chy �f �����������<br />
is c��p���������y i�c������� i� �h�� ����h-��as� pa�� �f<br />
��c�����i�� 8 �W��s����� ���-a��pi��� �����ai�s���<br />
c��p�isi�� ����i��s ��i��� �h�� Eif������ �h�� H��s��c��� �h��<br />
���������s�� �h�� P��a���a� ����ai��� �h�� V�s���s a�� �h��<br />
�assif c�����a��. N��v����h������ss�� �� �h�� �asis �f specific<br />
����-���ph�����ica�� a�� c��i�a�ic c���i�i��s�� �h��<br />
c�����y is ��a�i�i��a����y �ivi���� i��� �w� �ai�<br />
��c�����i��s�� �h�� O��s��i�� i� �h�� ����h a�� �h��<br />
G����a�� i� �h�� s���h. Wi�hi� �h�� G����a���� which<br />
is cha�ac����i����� �y a ����� h���������������s ��������y<br />
i� c��pa�is�� �� �h�� O��s��i���� �w� s��-��c�����i��s<br />
may be further distinguished: the Minette basin<br />
a�� �h�� ��s�������� va������y ����i�is��a�i�� ���s Ea��<br />
��� F��ê�s 2003�.<br />
����� f���shwa���� �ac��i�v��������a���s�� �h��<br />
caddisflies (<strong>Trichoptera</strong>) constitute one of the most<br />
diversified groups. Only aquatic Diptera approach<br />
�� ���c����� �h�� T�ich�p����a i� ������� �f sp��ci��s ��<br />
�������a. Th�s�� �h�� T�ich�p����a �isp��ay ��c�����ica��<br />
a�� ���havi���a�� sp��cia��isa�i��s which ���a�����<br />
�h��� �� s�cc��ssf�����y c�����is�� a vas� �a���� �f ����ic<br />
a�� ������ic wa����s ���.�. �ac�ay & Wi��i�s 1979��<br />
������ 1989�. This hi�h �a�����ica�� �iv���si�y �f<br />
T�ich�p����a c��c���������y i���c��s a hi�h �iv���si�y<br />
�f ��if�� his���y s��a����i��s �ha� �a��� �his ����p ����<br />
�f �h�� ��s� s�i���� �� app�ais�� �h�� s���c����� a��<br />
f��c�i��i�� �f aq�a�ic ��c�sys����s ����s�� 2003�.<br />
Although caddisflies are present in a wide range of<br />
aq�a�ic ha�i�a�s�� ��������s sp��ci��s hav�� v���y s��ic�<br />
���vi��������a�� ���q�i��������s �R��sh & U���ic����<br />
197��� �a��ic�y 1981�� ������ 1989�� R��sh 1993�� D�h���<br />
2002�. F�� �his ���as�� a�� ���ca�s�� �f �h�� �s�a��<br />
high species diversity and density of caddisflies in<br />
��p���������� s��fac�� wa����s �� ���� ha���� a�� �h��i�<br />
�is��i���i��s a���� a����� �h�� s����a� c���i���� ��<br />
�h�� ��h��� ha���� ass������a���s �f T�ich�p����a app��a�<br />
as i���a�� i��ica���s �� ���s� �h�� i���a �ha� a� a p�i��i<br />
����i��a��i��a�i�� �f �h�� ��a��scap�� ca� ��� �s��� ��<br />
c��assify �i��ic c�����i�i��s.<br />
I� �his s���y�� �h�� a�i��i�y �f a ��a��scap��<br />
classification to explain variation in caddisfly<br />
sa�p����s c�������c���� f��� a���� 230 si���s �is��i������<br />
�v��� �h�� wh����� c�����y�� was c��pa���� �� �ha� �f a<br />
�iv��� �yp�����y ��������i���� �� �h�� �asis �f s������c����<br />
a�i��ic va�ia�����s �F�������� et al. 200��. F���h����������<br />
a ���f������c�� c���i�i�� app��ach was �s��� i� ������<br />
�� ���c���as�� �h�� hi�h h�������������i�y �ha� is ��i�����y<br />
to appear if patterns were derived from mixtures<br />
�f ���f������c�� a�� ������f������c�� si���s. I���������<br />
classification should rely on characteristics that<br />
a��� i���i�sic�� �� �a���a���� a�� a��� ��� �h�� ���s���� �f<br />
h��a� ac�ivi�i��s �G����i�s��� et al. 2000�. O��� �f<br />
<strong>Ferrantia</strong> • 55 / 2008
A. Dohet et al. Caddisfly assemblages characterizing different ecological areas in Luxembourg<br />
the primary purposes of classification for water<br />
���s���c�� �a�a�������� is �� ���v�����p app��p�ia���<br />
���p��c�a�i��s �f �i�����ica�� c���i�i��s�� �ha� is��<br />
�� p����ic� �h�� �a���a�� �� ���is������� ���f������c��<br />
c���i�i�� �Haw�i�s & N���is 2000�� Haw�i�s et al.<br />
2000�.<br />
O�� �ai� p��p�s�� is �� c��pa��� �h�� ��������� ��<br />
which distribution patterns of caddisflies within<br />
Luxembourg classified by large scale ecological<br />
areas compared with a classification by stream<br />
�yp��s a� a s�a������� spa�ia�� sca����. W�� a�����ss��� �h��<br />
following specific questions: 1) Do the traditional<br />
��c�����ica�� ����i��s ��s���v��� i� �����������<br />
correspond to distinct caddisfly assemblages? 2)<br />
D���s a s����a� �yp�����y ���a����� �� ��� �� cap�����<br />
more variation in caddisflies communities? 3) What<br />
a��� �h�� i�p��ica�i��s �f �h�� ���s����s f��� q���s�i��s<br />
1 a�� 2 f�� �h�� ���si�� a�� �s�� �f �i�����ica��<br />
assessments in aquatic ecosystem management?<br />
4� Wha� is �h�� p��p���i�� a�� wha� a��� �h��<br />
T�ich�p����a sp��ci��s�� which a��� cha�ac����is�ic �f �h��<br />
different landscape units resulting from the most<br />
robust classification?<br />
Material and methods<br />
Site selection and field sampling<br />
� �a�as����� c��p�isi�� physi�-������aphica����<br />
physica���� ch���ica�� a�� ��a�� �s�� va�ia�����s<br />
���as����� a� 239 sa�p��i�� si���s �is��i������ a���� �v���<br />
�h�� c�����y was �s���. Th��s�� 239 si���s w����� s������c����<br />
i� ������ �� p��vi��� a �������va�� a�� ���p���s����a�iv��<br />
hy�������ica�� a�� ������aphica�� c�v���a���.<br />
Although different degrees of human impact were<br />
considered, a particular effort was made to find<br />
s����a�s wi�h �i�i�a�� �is����a�c��. Th�� c��p�������<br />
��is� �f va�ia�����s ���as����� a� sa�p��i�� si���s ca� ���<br />
f���� i� F�������� et al. �200��.<br />
B����hic i�v��������a���s w����� sa�p����� a� ��ach<br />
s�a�i�� �wic�� a y��a� �sp�i�� a�� s������-a�����<br />
seasons) from the different microhabitats (riffles,<br />
depositional zones, different types of vegetation).<br />
Th�� sa�p��i�� p��c������� was ���sc�i���� i� D�h���<br />
et al. �2002�. C��c����i�� �a�����ic ���s�����i���� a����<br />
invertebrate taxa collected were identified mainly<br />
�� sp��ci��s ����v����. Th�� ���a�� ������� �f �a�a ���c������<br />
f��� �h�� 239 si���s was 966.<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Ecological areas in Luxembourg<br />
�cc���i�� �� �h�� ��p�c��i�a��� a�� ��a��scap��<br />
f��a�����s s�ch as ��p���aphy�� ��������y�� a�� ��a��<br />
c�v����� �w� ��a���� ��c�����ica�� a���as�� which a���<br />
characterized by specific geo-morphological and<br />
c��i�a�ic c���i�i��s�� ca� ��� ���c���i����� i� �h�� G�a��<br />
D�chy �f ����������� �Fi�. 1a�. Th�� O��s��i�� i�<br />
�h�� ����h c�v���i�� ����-�hi�� �f �h�� �����i���y is a<br />
h�����������s schis���s H���cy�ia� �assif wi�h a<br />
���a� a���i����� app��achi�� 4�0 �. Th�� ����ai�i��<br />
�f �h�� �����i���y is cha�ac����i����� �y T�iassic a��<br />
J��assic ��ay���s �� a D��v��ia� �as��. Th�� a���i�����<br />
va�i��s ����w����� 2�0 � a�� 400 �. B��ca�s�� �f �h��<br />
different altitudinal ranges between these to main<br />
ecological areas, rivers flowing in the northern<br />
pa�� a��� cha�ac����i����� �y �����p��� va������ys i�<br />
comparison to the rivers flowing in the southern<br />
part. Minette basin and Moselle valley, which can<br />
��� assi�i��a���� as �w� s��-��c�����i��s p����ai�i��<br />
�� �h�� G����a�� �ai� ��c�����i���� a��� ���s��ic����<br />
���sp��c�iv����y �� �h�� s���hw��s� a�� s���h��as� �f �h��<br />
country. The Minette basin also called �red soils�<br />
is cha�ac����i����� �y �a��s a�� sa��s�����s c�v������<br />
wi�h f������s s���i�����s. This a���a is a� ���� �i�i��<br />
�is��ic�. �as���y�� �h�� ��s�������� �asi� is ���s��ic���� ��<br />
�h�� s���h��as� a�� �cc�pi��s ����y 1% �f �h�� ��a��<br />
s��fac�� �f �h�� c�����y. This a���a �a���s a�va��a���<br />
�f a c����a���y ��i��� a�� s���i��� c��i�a��� a�� is a��s�<br />
cha�ac����i����� �y a hi�h p��p���i�� �f vi���ya��s��<br />
which ���p���s���� a���� 36% �f �h�� s��fac�� a���a �f<br />
�his ����i��. I� �h�� s���h���� pa�� �f �h�� c�����y��<br />
��ay���s �f sa��s�����s a�� �a��s a�������a��� wi�h<br />
c��ays i�v���vi�� ����� �i����a��i����� s����a� wa����<br />
i� c��pa�is�� �� �h�� ����h pa��. ������v����� �h��<br />
differences in topology, geology and climate<br />
also involve different land uses in the country<br />
a�� ���ha�c�� �h�� pa��i�i�� ����w����� �h�� �w� �ai�<br />
��c�����ica�� a���as �i.��.�� O��s��i�� a�� G����a���.<br />
I��������� �h�� ����h ���i�� ��ss����ia����y a f����s����<br />
area is generally less influenced by anthropogenic<br />
�is����a�c��s i� c��pa�is�� �� �h�� s���h wh�����<br />
�i� ci�i��s�� i���s��i��s a�� i�����siv�� a��ic�������� a���<br />
c��c�����a����.<br />
Ev��� if �h�� 239 si���s a��� �is��i������ �v��� �h�� wh�����<br />
c�����y�� ��f�����a�����y �� ���� is i�c������� i� �h��<br />
��s�������� �asi� ��c�����ica�� a���a �Fi�. 1a�. �c��a����y�� �h��<br />
Moselle is a very wide river and requires a specific<br />
sa�p��i�� p��c������� �ha� was ��� c��pa�i����� wi�h<br />
�h�� ���� �s��� f�� �h�� s����a�s i�v��s�i�a���� i� �his<br />
s���y.<br />
35
A. Dohet et al. Caddisfly assemblages characterizing different ecological areas in Luxembourg<br />
36<br />
Typology<br />
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(a)<br />
Oesling Oesling Oesling<br />
Minette Minette Minette basin basin basin<br />
I� �h�� c������� �f �h�� WFD i�p���������a�i�� �EU<br />
2000), an optimal �a priori� classification of streams<br />
in Luxembourg was defined and validated upon<br />
physi�-������aphica�� va�ia�����s �F�������� et al. 200��.<br />
O���y ���s�����ica�� �a�a w����� c��si������� s� as ��<br />
p���s���v�� �h�� i����p�������c�� ����w����� �i��ic a��<br />
a�i��ic �a�a. I� sh����� ���h c��assica�� a�� �����<br />
c��p����� s�a�is�ica�� �����s w����� �s��� i� ������ ��<br />
i�����ify a� �p�i�a�� s��pa�a�i�� �f s����a� �yp��s ��<br />
�h�� �asis �f ���s�����ica�� va�ia�����s �����a���� �� ��������y��<br />
������va�i�� a�� �����i���i�a�� s����a� ��a�i����. This<br />
resulted in the definition of six stream types for<br />
�h�� wh����� c�����y �Fi�. 1��. Typ�����ica�� ���ys<br />
w����� p�i�cipa����y �h�� �����a�� si���� �f �h�� s����a��� �h��<br />
altitude and the water mineralization. The latter<br />
was well correlated to the geological difference<br />
����w����� �h�� ca��ca�����s a�� ���-ca��ca�����s a���as<br />
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Moselle Moselle Moselle valley valley valley<br />
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Typology<br />
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Type IV<br />
Type V<br />
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Altitude<br />
< 150 m<br />
150 - 250 m<br />
250 - 350 m<br />
350 - 450 m<br />
450 - 550 m<br />
> 550 m<br />
Fig. 1: (a) Map of Luxembourg showing the four ecological areas of the country: the Oesling (in green),<br />
the Gutland (in red), the Minette basin (in yellow) and the Moselle valley (in blue). The 239 sampling<br />
sites are superposed on the landscape classification. (b) Stream typology of the Grand-Duchy of Luxembourg<br />
on the basis of abiotic variables. Type I, small high-altitude streams in the Oesling; Type II,<br />
small mid-altitude streams in the Oesling; Type III, mid-sized mid-altitude streams in the Oesling; Type<br />
IV, small-sized mid-altitude streams in the Gutland; Type V, mid-sized low and mid-altitude streams in<br />
the Gutland; Type VI, large lowland streams.<br />
�f �h�� c�����y. ����� �h���sh���� va�����s �f �������va��<br />
���vi��������a�� va�ia�����s ���ai���� f��� a ���p����<br />
graphical analysis performed on the different<br />
s����a� �yp��s�� a��� �iv��� i� �a����� 1. �cc���i��<br />
�� �h�� �i����a��i��a�i�� �f wa���� ���.�. ca����a���<br />
ha�����ss�� c����c�ivi�y��� s����a� �yp��s I�� II a��<br />
III ����w �i����a��i��a�i��� ca� ��� c����a���y s��pa�a����<br />
f��� �yp��s IV�� V a�� VI �hi�h �i����a��i��a�i���.<br />
I� ��ach �f �h��s�� �w� s������ps�� �h�� si���� ��a�i����<br />
���.�. ca�ch����� a���a�� �is�a�c�� �� s���c���� wi��h<br />
�f �h�� �iv���� ���a�����s �� sp��i� s����a� �yp��s I�� II<br />
a�� IV �s�a���� s����a� �yp��s� f��� �yp��s III a��<br />
V �i���������ia��� s����a� �yp��s� a�� �yp�� VI ���a����<br />
s����a� �yp���. Fi�a����y�� s����a� �yp��s I a�� II ca� ���<br />
discriminated upon the elevation values: sites of<br />
�h�� s����a� �yp�� I ���i�� si��a���� a� hi�h��� a���i�����s<br />
�ha� si���s �f �h�� s����a� �yp�� II.<br />
<strong>Ferrantia</strong> • 55 / 2008
A. Dohet et al. Caddisfly assemblages characterizing different ecological areas in Luxembourg<br />
Tab 1: Threshold values of relevant environmental variables for the different stream types.<br />
Reference conditions<br />
The dataset was filtered by the criteria specified<br />
in table 2 to test the influence of the perturbation<br />
gradient on the robustness of the classification (i.e.,<br />
the degree to which the caddisfly communities<br />
are distinct along the different landscape<br />
classifications).<br />
T� ���s��ic� �h�� �a�a �� sa�p����s �f ���a�-�a���a��<br />
c���i�i��s�� a s���p �y s���p p��c������� was �s���.<br />
A first selection of sites was made on the basis of<br />
i�s����a� ����i���� c��c�����a�i��s �i.e.�� a����i����<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Typ��s<br />
Va�ia�����s Typ�� I<br />
Ca�ch����� a���a ��� 2 �<br />
Typ�� II<br />
Typ�� III<br />
2�% 2.9 2.8 182.7 3.2 80.1 310�.6<br />
����ia� �.0 9.6 346.9 9.1 117.4 3236.0<br />
7�% 11.7 31.9 431.3 19.4 263.7 4000.0<br />
2�% 1.0 1.� 9.2 1.0 6.8 36.�<br />
�����a� wi��h ��� ����ia� 1.� 2.0 13.7 2.0 8.� 39.9<br />
7�% 2.1 3.� 21.9 3.0 11.8 44.1<br />
2�% 372 2�4 247 23� 218 1�3<br />
����i����� ��� ����ia� 390 282 274 26� 240 16�<br />
7�% 431 310 330 278 260 177<br />
2�% 0.8 2.3 2.7 0.8 2.3 1.3<br />
����p�� ��.�� -1 � ����ia� 1.7 �.0 4.3 1.9 4.2 1.�<br />
7�% 2.3 6.6 6.2 3.1 6.9 2.3<br />
2�% 7.0 7.2 7.6 7.7 7.� 8.1<br />
pH ����ia� 7.2 7.� 7.8 7.9 7.8 8.2<br />
7�% 7.4 7.8 8.0 8.1 8.1 8.3<br />
2�% 1.1 1.2 1.0 �.4 �.2 �.0<br />
T��a�� ha�����ss ���q.� -1 � ����ia� 1.3 1.� 1.2 6.2 �.6 �.1<br />
7�% 1.� 2.0 1.� 7.6 6.7 �.2<br />
2�% 147 172 14� �7� �34 477<br />
Conductivity (µS.cm -1 � ����ia� 184 21� 177 664 600 483<br />
DBO � ���.� -1 �<br />
7�% 221 283 2�2 806 728 �31<br />
2�% 0.7 0.� 1.8 0.9 2.0 2.�<br />
����ia� 1.4 0.9 2.0 1.9 2.8 2.9<br />
7�% 2.6 1.4 3.4 3.4 10.6 3.2<br />
Typ�� IV<br />
Typ�� V<br />
Typ�� VI<br />
�i��i���s�� s��������� ���ac�iv�� ph�sph����s a�� DBO �<br />
�� s���a�i����� i� �h�� ���a�ic p�������i�� i�����<br />
�I.P.O.�� ���c�����cq & �aq���� 1987��. ���c����� �h��<br />
a��h��p�����ic ��a�� �s�� i� �h�� s�������i��s �f �h��<br />
sites was evaluated by drawing buffer strips along<br />
�h�� s����a� �f ��ach si����� acc���i�� �� T�w�s���� et<br />
al. �2003�. Each s��ip was �����i�i���� �y a �is�a�c�� ��<br />
��i�h��� si��� �f �h�� s����a� c������� ��i��� �f��� �0 �� 400<br />
�� a�� �y a �is�a�c�� ��w�s����a� �f��� 60 �� 130<br />
�� a�� �ps����a� �f��� �40 �� 1270 �� �f �h�� s���y<br />
si���. �a�� �s�� p��p���i��s w����� �h��� ��s�i�a����<br />
f��� a GI�. �a��-�s�� �a�a w����� ���ai���� f���<br />
�h�� �i�is��y �f �h�� E�vi�������� a�� ��i�i�a����<br />
37
A. Dohet et al. Caddisfly assemblages characterizing different ecological areas in Luxembourg<br />
38<br />
Tab 2: Criteria used to restrict the dataset to near-reference samples.<br />
Fi������ c�i����i�� R��as���� c�������<br />
I�s����a� ����i���� c��centration:<br />
I.P.O.<br />
E�c���si�� �f p����������<br />
����a�ic p�������i��� si���s<br />
Land use: L.U.I. E�c���si�� �f si���s wi�h<br />
�����a���� ca�ch�����<br />
Biotic index: (I.B.G.N.) E�c���si�� �f �����a����<br />
si���s<br />
Hydromorphology: SEQ<br />
physiq���<br />
E�c���si�� �f hy������ph�����ica����y<br />
�����a����<br />
si���s<br />
f��� �h�� EU CORINE p����a�. � �a�� Us�� I�����<br />
��.U.I.� was ca��c���a���� acc���i�� �� H���i�� et al.<br />
�2004� a�� F����� �2004� �y s���i�� 4 �i���s ���a�<br />
��a���� 2 �i���s c��p ��a�� a�� 1 �i��� pas����� ��a�� �s����<br />
ass��i�� �ha� ���a� ��a�� �s�� has a ����a���� i�pac�<br />
�ha� c��p ��a�� a�� pas�����s. Th����� �h�� physica��<br />
ha�i�a� �f �h��s�� p���-s������c���� s����a�s was ��va���a����<br />
in the field by the SEQphysique method (Agence<br />
��� �����a� ���a� ��a� Rhi�-����s�� Rhi�-����s�� Rhi�-����s�� 1998��� 1998��� 1998��� which a�����ws a�����ws a�����ws a� a� a� ��asy ��asy ��asy<br />
a�� fas� cha�ac����i��a�i�� �f �h�� physica�� q�a��i�y �f<br />
�iv��� ����s a�� �a��s �Cha��i��� et al. 2002�� Rav���<br />
et al. 2002�. Fi�a����y�� �h�� �a�a w����� ch��c���� wi�h<br />
�h�� �i��ic i����� I.B.G.N. ��FNOR 2004��� i� ������<br />
�� ����i�i�a��� s��v�������y i�pai���� si���s acc���i�� ��<br />
�����hic i�v��������a��� c�����i�i��s.<br />
This p��c������� ���a�����s �� ���s��ic� �h�� �a�as��� �� 62<br />
���a�-�a���a�� si���s. �s s���� s����a� �yp��s ���.�. s����a�<br />
types V and VI) did not hold sites with a su���cient<br />
hi�h q�a��i�y�� �h��y ��s� ��� c��si������� as �h�� hi�h��s�<br />
��c�����ica�� p������ia�� avai��a����� f�� �h��i� ���sp��c�iv��<br />
�yp��s. �c��a����y�� ��v��� if �h�� sa��� ����h�������y was<br />
�s��� �� s������c� �h�� ���s� ��c�����ica�� q�a��i�y si���s�� �h��<br />
�h���sh����s va�����s f�� s���� pa�a�������s ���.�. ��a��<br />
use index) were different for fast flowing mountain<br />
streams in comparison to slow-flowing lowland<br />
s����a�s f�� i�s�a�c�� �Ta�. 2�.<br />
Typ�� I<br />
Typ�� II<br />
Th���sh���� va�����s<br />
Typ�� III<br />
Statistical analysis<br />
Typ�� IV<br />
Typ�� V<br />
Typ�� VI<br />
>= 3.� >= 3.� >= 3.� >= 3.� >= 3.� >= 3.�<br />
= 12<br />
>= 60% >= 60% >= 60% >= 60% >= 60% >= 60%<br />
�����iva�ia��� s�a�is�ica�� ���ch�iq���s ��i��� PC�<br />
�P�i�cipa�� C��p������ ��a��ysis� w����� �s��� ��<br />
i�����s��a��� �h�� si��� s��pa�a�i�� ����iv��� f��� �h��<br />
�is�a�c�� �a��i�. Th��s�� ��a�i���� a�a��ys��s ���a����� ��<br />
visually assess the relative strength of the different<br />
classifications by comparing the distinctness of<br />
their patterns in the ordination plots (Waite et<br />
al. 2000�. I� ��i��f�� �h��s�� ���ch�iq���s q�a��ify �h��<br />
difference between any two communities by<br />
c��pa�i�� �h�� a����a�c�� �f ��ach �a��� p���s����<br />
i� ��ach �f �h�� �w� c�����i�i��s�� a�� a������a�i��<br />
�his s��� �f c��pa�is��s i��� a �is�a�c�� ���as����.<br />
�� ���i�a�i�� �f �his �is�a�c�� �a��i� wi���� sh�w<br />
c��p�si�i��a����y v���y si�i��a� c�����i�i��s c���s��<br />
������h��� i� �h�� ���i�a�i�� spac���� wh�����as v���y<br />
different communities will be spread across the<br />
p����. I� �h�� ���i�a�i�� p��a��� �h�� s�p���p�si�i�� �f a�<br />
inertia ellipse based on the average plotting position<br />
of each landscape class, enables to differentiate<br />
strong classifications (each class is well separated<br />
i� �h�� ���i�a�i�� spac�� a�� c�����sp���s �� �is�i�c�<br />
c�����i�i��s� f��� w��a� ����s �����a� �v�����ap<br />
����w����� �h�� c��ass��s�� a�s���c�� �f �isc������ c���s����s�.<br />
Ra��� sp��ci��s�� wh�s�� �cc������c�� is �s�a����y<br />
����� a matter of chance than an ecological<br />
i��ica�i�� �Ga�ch 1982��� w����� ��� ����ai���� f��<br />
<strong>Ferrantia</strong> • 55 / 2008
A. Dohet et al. Caddisfly assemblages characterizing different ecological areas in Luxembourg<br />
these multivariate analyses. Caddisfly species<br />
�ha� �cc������ i�
A. Dohet et al. Caddisfly assemblages characterizing different ecological areas in Luxembourg<br />
g 2<br />
40<br />
a��� ��� �a���� i��� acc���� i� �his ���a� ��a��scap��<br />
classification. Obviously, these gradients are likely<br />
to influence significantly caddisfly assemblages.<br />
Stream typology<br />
(a)<br />
The two first eigenvalues are identical to those of<br />
�h�� p���vi��s ���i�a�i�� �i.��.�� ���sp��c�iv����y 9.32%<br />
a�� 4.78% �f �h�� i�����ia; Fi�. 3�. Th�� ���as�� is �ha�<br />
si���s a��� �is��i������ i� �h�� ���i�a�i�� spac�� �� �h��<br />
basis of the same caddisfly communities than in<br />
1<br />
2<br />
3<br />
(b)<br />
Fig. 2: Ordination of sites and ecological areas by principal component analysis (PCA1). (a) Histogram<br />
of eigenvalues ; (b) distribution of 239 samples (small dots) and the three ecological areas (open circles)<br />
on the plane of the first two axes (C1 first eigenaxis; C2 second eigenaxis). Ecological areas are<br />
positioned at the weighted average of samples representing them (1: Oesling; 2: Gutland; 3: Minette<br />
basin).<br />
the first PCA. Only the classification, indicated by<br />
���w i�����ia ������ips��s�� has cha����� i� c��pa�is��<br />
�� �h�� PC�1. �����a� �yp��s I a�� II ca� ��� ���<br />
�is�i���ish��� a�� �h����� is s�i���� s���� �v�����ap<br />
����w����� s����a� �yp��s IV a�� V �� ���� ha�� a��<br />
����w����� s����a� �yp��s IV + V a�� I + II �� �h�� ��h���<br />
hand. Nevertheless, clusters are generally better<br />
s��pa�a���� �ha� i� �h�� p���vi��s ���i�a�i�� �as���<br />
�� ��c�����ica�� a���as a������ �PC�1�. I� pa��ic���a���<br />
��a����� �iv���s ��������i�� �� s����a� �yp��s III a��<br />
VI ����sp��c�iv����y�� �i� si����� �i� a���i����� s����a�s<br />
i� �h�� O��s��i�� a�� ��a���� ���w��a�� s����a�s� a���<br />
<strong>Ferrantia</strong> • 55 / 2008
g 3<br />
A. Dohet et al. Caddisfly assemblages characterizing different ecological areas in Luxembourg<br />
C1<br />
w������ s��pa�a���� i� �h�� ���i�a�i�� �ia��a� a��<br />
correspond to specific caddisfly assemblages.<br />
Stream typology and reference<br />
condition<br />
Wh��� si���s c��si������� �� ��� ����� �� ����ss i�pac����<br />
a��� �����v��� f��� �h�� �a�as����� ����y a���� 3�% �f<br />
sites are still available to test the influence of the<br />
p�������a�i�� ��a�i���� �� �h�� �����a�i�� ����w�����<br />
s����a� �yp��s a�� T�ich�p����a �is��i���i��s. I�<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
(a)<br />
III<br />
VI<br />
C2<br />
V<br />
II<br />
IV<br />
I<br />
(b)<br />
Fig. 3: Ordination of sites and stream types by principal component analysis (PCA2). (a) Histogram of<br />
eigenvalues ; (b) distribution of 239 samples (small dots) and the six stream types (open circles) on the<br />
plane of the first two axes (C1 first eigenaxis; C2 second eigenaxis). Stream types are positioned at the<br />
weighted average of samples representing them (numbers refer to stream type codes in table 1).<br />
pa��ic���a��� �his s������c�i�� ����i�i�a���s ��������s<br />
si���s ��������i�� �� �h�� s����a� �yp��s V a�� VI ��i�<br />
si����� ���w a�� �i� a���i����� s����a�s i� �h�� G����a��<br />
and large lowland streams). For the latter stream<br />
�yp���� �� si���s ca� ��� c��si������� as "���f������c��" s�<br />
far. Consequently, the stream type VI was omitted<br />
f��� �his ���w ���i�a�i�� �PC�3; Fi�. 4�<br />
If �h�� a�a��ysis is ���s��ic���� �� ���a�-���f������c�� si���s<br />
in the different stream types (Fig. 4), some clusters<br />
are noticeably better separated. The eigenvalues<br />
are noticeably higher in this ordination (C1:<br />
41
Fig 4<br />
A. Dohet et al. Caddisfly assemblages characterizing different ecological areas in Luxembourg<br />
42<br />
C1<br />
(a)<br />
Fig. 4: Ordination of sites in �reference �reference reference condition� condition� condition� and stream types by principal component analysis<br />
(PCA3). (a) Histogram of eigenvalues; (b) distribution of 62 samples (small dots) and the five stream<br />
types (open circles) on the plane of the first two axes (C1 first eigenaxis; C2 second eigenaxis). Stream<br />
types are positioned at the weighted average of samples representing them (numbers refer to stream<br />
type codes in table 1).<br />
13.64% and C2: 6.00%, Fig. 4) indicating that a<br />
hi�h��� a����� �f �i��ic va�ia�i�� is cap������ �y<br />
the classification when only near-natural sites are<br />
s������c����. I� c��pa�is�� �� �h�� p���vi��s ���i�a�i��<br />
�PC�2��� �h�� s��pa�a�i�� is ��vi��s��y i�p��v��� f��<br />
s����a� �yp��s IV a�� V ����sp��c�iv����y�� s�a���� si�����<br />
�i� a���i����� s����a�s i� �h�� G����a�� a�� �i� si�����<br />
���w a�� �i� a���i����� s����a�s i� �h�� G����a���<br />
indicating now distinct caddisfly assemblages.<br />
Overall, there is a better separation of the stream<br />
�yp��s ��������i�� �� �h�� �w� �ai� ��c�����ica�� a���as��<br />
�h�� O��s��i�� �s����a� �yp��s I�� II a�� III� a�� �h��<br />
G����a�� �s����a� �yp��s IV a�� V�. H�w��v����� ��v���<br />
i� ���a�-���f������c�� c���i�i���� s����a� �yp��s I a�� II<br />
����sp��c�iv����y�� s�a���� hi�h a���i����� a�� s�a���� �i�<br />
a���i����� s����a�s�� ���h i� �h�� O��s��i��� ca� s�i���� ���<br />
��� �is�i���ish��� �� �h�� �asis �f �h��i� T�ich�p����a<br />
c�����i�i��s.<br />
V<br />
C2<br />
III I<br />
Identification of characteristic<br />
caddisfly assemblages<br />
Characteristic caddisfly species are identified<br />
f�� c���s����s �s����a� �yp��s� ��s���v��� i� PC�2<br />
����i�a�i�� �f a���� si���s �f ��� �a�as���� a�� PC�3<br />
����i�a�i�� �f si���s i� "���a�-���f������c�� c���i�i��"�.<br />
The lists of indicator species for different stream<br />
�yp��s a��� p��vi���� i� �a����� 3 f�� a���� si���s a�� �a����� 4<br />
f�� si���s c��si������� as "���a�-���f������c��".<br />
�i�c���� s����a� �yp��s I a�� II ca���� ��� �is�i���ish���<br />
on the basis of their caddisfly fauna, they were<br />
�������� ���f���� �h�� c��p��a�i�� wi�h �h�� INDV��<br />
����h��. �p��ci��s a��� s������ acc���i�� �� �h��<br />
����ps �h��y a��� i��ica�iv�� f�� �asc����i��� a�� �y<br />
��s���v��� i��ica��� va����� ����sc����i���. F�� ��ach<br />
sp��ci��s�� i��ica��� va�����s a��� �iv��� f�� �h�� s����a�<br />
type with the highest a���nity but also for all other<br />
IV<br />
II<br />
(b)<br />
<strong>Ferrantia</strong> • 55 / 2008
A. Dohet et al. Caddisfly assemblages characterizing different ecological areas in Luxembourg<br />
s����a� �yp��s. �p��ci��s �ha� a��� c��si������� as ����s�<br />
indicators of a particular stream type (p ≤ 0.05 and<br />
indicator value ≥ 25) are marked in bold characters<br />
�Ta�. 3 - 4�.<br />
Nine caddisfly species (Sericostoma personatum/<br />
schneideri�� Glossosoma conformis N����iss 1963��<br />
Hydropsyche instabilis�� Odontocerum albicorne�� Agapetus<br />
fuscipes�� Philopotamus ludificatus �c�ach��a��� 1878��<br />
Potamophylax cingulatus �����ph���s�� 1837��� Oecismus<br />
monedula �Ha������ 18�9� a�� Silo pallipes �Fa��ici�s��<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
1781)) can be considered as significant indicators<br />
f�� �h�� s����a� �yp�� I+II �s�a���� hi�h a���i����� a��<br />
�i� a���i����� s����a�s i� �h�� O��s��i����� wh��� a���� si���s<br />
�f �h�� �a�a�as�� a��� s������c���� �Ta�. 3�. If �h�� a�a��ysis<br />
is restricted to sites identified as �reference�, six<br />
species remain significant indicators (G. conformis��<br />
P. ludificatus�� S. personatum/schneideri�� H. instabilis�� O.<br />
monedula a�� O. albicorne� f�� �h�� s����a� �yp�� I+II.<br />
N�������s sp��ci��s �1�� a��� cha�ac����is�ic �f �h��<br />
s����a� �yp�� III ��i� si������� �i� a���i����� s����a�s i�<br />
Tab. 3: List of indicator species for different stream types according to the PCA2. The �Avg� �Avg� Avg� and �Max� �Max� �Max� �Max� Max�<br />
columns refer to the indicator values for the given species (average and maximum value);<br />
�MaxGrp� MaxGrp� is the type identifier for the group with the highest indicator value. The statistical<br />
significance of the observed indicator value is tested with a randomization (Monte Carlo)<br />
procedure: �SD� �SD� SD� is the Standard Deviation; �P� �P� �P� �P� P� evaluates evaluates the the statistical statistical significance significance of of the<br />
the<br />
maximum indicator value recorded for given species. The probability of type I error is the<br />
proportion of times that the maximum indicator value from the randomized data set equals<br />
or exceeds the maximum indicator value from the actual data set. Species are ordered according<br />
to the groups they are indicative for (ascending) and by observed indicator value<br />
(descending). Significant indicators for a particular stream type (IndVal ≥ 25.0 and p ≤ 0.05)<br />
are marked in bold characters.<br />
Types I+II III IV V VI Observed<br />
Number of items 89 32 66 36 6 IndVal<br />
Avg Max Max-<br />
Grp<br />
IndVal from<br />
randomized<br />
groups<br />
Mean SD<br />
Sericostoma personatum/schneideri 17 55 I+II 55 24 4 0 0 55,3 21,0 5,49 0,002<br />
Glossosoma conformis 9 45 I+II 45 0 0 0 0 44,8 10,4 5,38 0,002<br />
Hydropsyche instabilis 9 41 I+II 41 0 1 5 0 40,9 14,2 6,30 0,010<br />
Odontocerum albicorne 9 39 I+II 39 0 4 4 0 38,6 13,6 5,34 0,008<br />
Agapetus fuscipes 7 33 I+II 33 0 3 0 0 33,1 16,3 5,97 0,014<br />
Philopotamus ludificatus 6 31 I+II 31 0 0 0 0 31,5 8,0 4,81 0,005<br />
Potamophylax cingulatus 8 29 I+II 29 0 13 0 0 29,1 13,0 5,34 0,027<br />
Oecismus monedula 5 27 I+II 27 0 0 0 0 27,0 7,4 4,75 0,011<br />
Silo pallipes 6 25 I+II 25 0 4 0 0 25,2 10,5 5,30 0,027<br />
Hydropsyche saxonica 8 20 I+II 20 0 1� � 0 20��4 14��7 ���22 0��106<br />
Philopotamus montanus 4 20 I+II 20 0 0 0 0 19��6 6��9 4��74 0��04�<br />
Halesus digitatus 6 18 I+II 18 3 11 1 0 18��2 14��2 6��08 0��1�7<br />
Hydropsyche fulvipes 4 17 I+II 17 0 4 0 0 17��0 8��7 ���04 0��077<br />
Rhyacophila praemorsa 3 13 I+II 13 0 1 0 0 13��1 6��� 4���4 0��066<br />
Potamophylax latipennis 4 12 I+II 12 4 1 0 0 12��0 8��6 4��91 0��1�9<br />
Hydatophylax infumatus 2 9 I+II 9 0 0 0 0 9��� ���8 4��26 0��091<br />
Anomalopterygella chauviniana 3 9 I+II 9 7 0 0 0 9��2 7��0 4��99 0��171<br />
P<br />
43
A. Dohet et al. Caddisfly assemblages characterizing different ecological areas in Luxembourg<br />
44<br />
Types I+II III IV V VI Observed<br />
Number of items 89 32 66 36 6 IndVal<br />
Avg Max Max-<br />
Grp<br />
IndVal from<br />
randomized<br />
groups<br />
Mean SD<br />
Crunoecia irrorata 2 8 I+II 8 0 0 0 0 7��9 4��4 4��29 0��117<br />
Hydropsyche silfvenii 1 7 I+II 7 0 0 0 0 6��7 4��0 3��32 0��10�<br />
Wormaldia occipitalis/subnigra 1 7 I+II 7 0 1 0 0 6��6 ���1 4��00 0��168<br />
Limnephilus fuscicornis 1 6 I+II 6 0 0 0 0 ���8 4��6 3��98 0��173<br />
Diplectrona felix 1 6 I+II 6 0 0 0 0 ���6 3��9 3��00 0��1�2<br />
Silo nigricornis 1 6 I+II 6 0 0 0 0 ���6 3��8 3��84 0��149<br />
Limnephilus extricatus 1 � I+II � 0 1 0 0 ���0 4��9 3��91 0��322<br />
Agapetus delicatulus 1 4 I+II 4 0 0 0 0 4��� 3��3 3��23 0��198<br />
Philopotamus variegatus 1 4 I+II 4 0 0 0 0 4��� 3��6 3��91 0��179<br />
Micropterna lateralis 1 4 I+II 4 0 0 0 0 4��� 3��6 3��71 0��208<br />
Adicella reducta 1 4 I+II 4 0 0 1 0 4��3 4��1 3��76 0��273<br />
Notidobia ciliaris 1 4 I+II 4 0 1 0 0 3��9 4��6 3��46 0��489<br />
Plectrocnemia geniculata 1 3 I+II 3 0 0 0 0 3��4 3��2 3���4 0��267<br />
Limnephilus rhombicus 1 3 I+II 3 0 0 0 0 3��1 4��3 3���1 0���17<br />
Enoicyla pusilla 0 2 I+II 2 0 0 0 0 2��2 2��7 3��03 0��470<br />
Synagapetus iridipennis 0 2 I+II 2 0 1 0 0 1��8 3��� 3��97 0��643<br />
Limnephilus centralis 1 2 I+II 2 0 1 0 0 1��8 3��4 3��36 0��618<br />
Tinodes cf. dives 0 1 I+II 1 0 0 0 0 1��1 2��3 2��77 1��000<br />
Micrasema longulum 0 1 I+II 1 0 0 0 0 1��1 2��2 2��49 1��000<br />
Limnephilus flavicornis-Gr. 0 1 I+II 1 0 0 0 0 1��1 2��2 2��69 1��000<br />
Apatania muliebris helvetica 0 1 I+II 1 0 0 0 0 1��1 2��2 2��49 1��000<br />
Beraea pullata 0 1 I+II 1 0 0 0 0 1��1 2��2 2��49 1��000<br />
Lepidostoma hirtum 19 83 III 1 83 0 3 7 82,7 18,5 7,30 0,001<br />
Oecetis testacea 17 80 III 1 80 0 0 2 79,9 10,1 5,39 0,001<br />
Brachycentrus maculatus 14 71 III 0 71 0 0 0 71,1 9,8 5,26 0,001<br />
Mystacides azureus 17 69 III 1 69 0 0 17 68,5 12,6 5,61 0,001<br />
Silo piceus 14 60 III 4 60 0 4 0 59,8 15,8 6,11 0,003<br />
Polycentropus flavomaculatus 18 55 III 0 55 0 1 32 54,5 11,8 5,41 0,002<br />
Lasiocephala basalis 12 54 III 1 54 0 5 0 54,4 15,1 7,21 0,003<br />
Brachycentrus subnubilus 10 49 III 0 49 0 0 0 49,3 6,2 4,38 0,002<br />
Hydropsyche siltalai 17 44 III 9 44 1 18 14 44,2 20,1 5,31 0,005<br />
Athripsodes cinereus 12 36 III 0 36 0 2 24 35,7 8,2 4,59 0,004<br />
Psychomyia pusilla 10 33 III 0 33 0 1 14 33,4 7,7 4,75 0,007<br />
Allogamus auricollis 6 31 III 0 31 0 0 0 30,7 6,2 4,20 0,009<br />
Ceraclea annulicornis 12 30 III 0 30 0 0 28 30,2 7,3 4,50 0,004<br />
Anabolia nervosa 7 29 III 5 29 0 0 0 28,7 8,2 4,41 0,009<br />
P<br />
<strong>Ferrantia</strong> • 55 / 2008
A. Dohet et al. Caddisfly assemblages characterizing different ecological areas in Luxembourg<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Types I+II III IV V VI Observed<br />
Number of items 89 32 66 36 6 IndVal<br />
Avg Max Max-<br />
Grp<br />
IndVal from<br />
randomized<br />
groups<br />
Mean SD<br />
Micrasema setiferum 6 28 III 0 28 0 0 0 28,1 4,8 4,05 0,005<br />
Athripsodes bilineatus 6 21 III 7 21 0 0 0 21��0 9��7 ���34 0��032<br />
Potamophylax luctuosus 4 20 III 0 20 0 0 0 19��7 6��2 4���7 0��032<br />
Halesus tesselatus 4 19 III 0 19 0 0 2 19��2 6��2 4��22 0��023<br />
Agapetus ochripes 3 14 III 0 14 0 0 0 14��4 ���8 3��87 0��042<br />
Goera pilosa � 13 III 2 13 2 0 6 13��3 8��9 ���74 0��114<br />
Leptocerus tineiformis 3 13 III 0 13 0 0 0 12��� 3��3 3��47 0��047<br />
Leptocerus interruptus 2 9 III 0 9 0 0 0 9��4 2��9 3��2� 0��069<br />
Setodes argentipunctellus 1 6 III 0 6 0 0 0 6��2 2��6 2��94 0��061<br />
Chaetopteryx major 2 6 III 0 6 � 0 0 ���8 6��0 4��44 0��329<br />
Cyrnus trimaculatus 1 � III 0 � 0 1 0 4��8 3��1 3��63 0��144<br />
Beraeodes minuta 2 4 III 4 4 3 0 0 4��3 7��0 4���1 0��776<br />
Chaetopteryx villosa 12 37 IV 13 9 37 2 0 37��1 26��6 8��1� 0��080<br />
Plectrocnemia conspersa 7 31 IV 5 0 31 0 0 31,4 11,9 5,72 0,018<br />
Tinodes unicolor 6 31 IV 0 0 31 0 0 30,6 8,3 4,89 0,007<br />
Drusus annulatus 7 26 IV 10 0 26 0 0 25,5 12,0 5,92 0,035<br />
Tinodes cf. rostocki 3 16 IV 0 0 16 0 0 16��� ���4 4��31 0��026<br />
Halesus radiatus 8 1� IV 11 6 1� � 2 1���� 1���� 6��02 0��34�<br />
Potamophylax latipennis/luctuosus � 12 IV 3 7 12 3 0 11��6 11��6 ���33 0��366<br />
Rhyacophila tristis 2 10 IV 0 0 10 0 0 10��3 ���2 3��97 0��066<br />
Limnephilus lunatus 3 10 IV 2 0 10 0 1 10��3 8��� 4��63 0��237<br />
Lithax obscurus 2 8 IV 0 0 8 0 0 7��6 4��0 3���4 0��079<br />
Micropterna sequax 1 6 IV 1 0 6 0 0 6��1 4��4 3��44 0��21�<br />
Synagapetus dubitans 1 � IV 0 0 � 0 0 4��� 3��1 3��18 0��1�4<br />
Melampophylax mucoreus 1 4 IV 0 0 4 0 0 4��0 3��9 3��67 0��286<br />
Mystacides cf. longicornis 1 3 IV 0 0 3 0 0 3��0 2��7 2��9� 0��282<br />
Tinodes cf. pallidulus 0 2 IV 0 0 2 0 0 1��� 2��2 2��73 0��613<br />
Ironoquia dubia 0 2 IV 0 0 2 0 0 1��� 2��3 2���7 0��663<br />
Limnephilus affinis-Gr. 0 2 IV 0 0 2 0 0 1��� 2��1 2��17 0��616<br />
Limnephilus bipunctatus 0 2 IV 0 0 2 0 0 1��� 2��2 2��49 0���99<br />
Micropterna nycterobia 0 2 IV 0 0 2 0 0 1��� 2��3 2���7 0��663<br />
Lithax niger 0 2 IV 0 0 2 0 0 1��� 2��2 2���0 0��600<br />
Glyphotaelius pellucidus 0 1 IV 0 0 1 0 0 0��9 2��9 3��67 1��000<br />
Stenophylax permistus 0 1 IV 0 0 1 0 0 0��9 2��9 3��63 1��000<br />
Hydropsyche pellucidula 9 37 V 3 2 0 37 4 37,5 12,2 5,57 0,008<br />
Hydropsyche angustipennis 4 22 V 0 0 0 22 0 21,5 8,1 4,58 0,016<br />
Hydroptila sp. 8 1� V 0 0 13 1� 11 1���0 20��8 7��73 0��789<br />
Mystacides nigra 3 12 V 0 4 0 12 2 11��9 6��3 4��4� 0��064<br />
Hydroptila vectis 3 11 V 0 0 4 11 0 10��7 ���9 3��99 0��09�<br />
Mystacides longicornis/nigra 4 9 V 1 7 0 9 4 9��2 7��7 ���00 0��200<br />
Lype reducta 2 7 V 0 3 1 7 0 7��2 ���8 4��12 0��198<br />
P<br />
45
A. Dohet et al. Caddisfly assemblages characterizing different ecological areas in Luxembourg<br />
46<br />
Types I+II III IV V VI Observed<br />
Number of items 89 32 66 36 6 IndVal<br />
IndVal from<br />
randomized<br />
groups<br />
Avg Max Max-<br />
Grp<br />
Mean SD<br />
Ithytrichia lamellaris 1 7 V 0 0 1 7 0 6��6 4��3 3���4 0��121<br />
Brachycentrus montanus 2 6 V 3 0 0 6 0 ���8 ���0 4��24 0��241<br />
Annitella obscurata 2 � V 0 1 2 � 0 ���4 ���3 3��36 0��34�<br />
Tinodes waeneri 1 3 V 2 1 0 3 0 2��7 4��9 3���4 0��76�<br />
Hydropsyche incognita 19 72 VI 0 22 0 1 72 71,9 11,3 5,40 0,001<br />
Hydropsyche contubernalis 16 72 VI 0 0 0 7 72 71,7 6,6 4,86 0,001<br />
Oecetis notata 13 65 VI 0 0 0 0 65 65,1 5,6 3,66 0,001<br />
Allotrichia pallicornis 9 44 VI 0 0 0 1 44 44,3 4,3 3,68 0,001<br />
Cheumatopsyche lepida 15 42 VI 0 33 0 0 42 41,7 7,7 4,77 0,001<br />
Rhyacophila fasciata/dorsalis-Gr. 18 35 VI 8 25 4 19 35 35,1 22,6 4,64 0,028<br />
Athripsodes albifrons 10 35 VI 0 12 0 4 35 34,7 8,7 4,77 0,006<br />
Ceraclea dissimilis 9 34 VI 0 12 0 2 34 33,7 7,5 4,67 0,005<br />
Ceraclea cf. fulva 3 17 VI 0 0 0 0 17 16��7 2��3 2��77 0��034<br />
Ceraclea nigronervosa 3 14 VI 0 1 0 0 14 14��3 3��2 3��18 0��0�0<br />
Agraylea sp. 3 14 VI 0 0 0 0 14 14��0 2��8 3��14 0��0�7<br />
Hydropsyche dinarica 2 � VI 0 0 0 4 � ���3 ���3 3��90 0��3�0<br />
�h�� O��s��i��� i� �h�� f����� �a���� �f �h�� q�a��i�y ��a�i����.<br />
This ������� ���c���as��s �� ����y s��v��� sp��ci��s<br />
�Polycentropus flavomaculatus �Pic������ 1834��� Oecetis<br />
testacea �C���is�� 1834��� Brachycentrus maculatus��<br />
Mystacides azureus ��i��a���s�� 1761��� Allogamus<br />
auricollis �Pic������ 1834��� Athripsodes bilineatus<br />
��i��a���s�� 17�8� a�� Ceraclea annulicornis �����ph���s��<br />
1836�� wh��� "���f������c��" si���s a��� s������c����. H�w��v�����<br />
among the latter species, an increase in the indicator<br />
va����� is ����y ��s���v��� f�� A. bilineatus wh��� �h��<br />
��s� �����a���� si���s a��� �����v���.<br />
The number of species in caddisfly assemblages<br />
�ha� a��� cha�ac����is�ic �f s����a� �yp��s ��������i��<br />
�� �h�� G����a�� ��c�����i�� is ���ic��a���y �����c���<br />
�s����a� �yp��s IV a�� V i� pa��ic���a��. I��������� ����y<br />
Plectrocnemia conspersa �C���is�� 1834��� Tinodes unicolor<br />
�Pic������ 1834� a�� Drusus annulatus ����ph���s�� 1837<br />
show relative high a���nities for the stream type IV<br />
�s�a���� si������� �i� a���i����� s����a�s i� �h�� G����a���<br />
a�� ����y Hydropsyche pellucidulla �C���is�� 1834� a��<br />
H. angustipennis �C���is�� 1834� a��� i��ica���s �f �h��<br />
s����a� �yp�� V ��i� si������� ���w a�� �i� a���i�����<br />
s����a�s i� �h�� G����a���. If �h�� i�pac���� si���s a���<br />
�����v��� f��� �h�� a�a��ysis�� P. conspersa a�� D.<br />
annulatus sh�w hi�h��� i��ica��� va�����s f�� s����a�<br />
�yp�� IV. P. cingulatus�� which was c��si������� as a<br />
cha�ac����is�ic sp��ci��s �f �h�� s����a� �yp�� I+II i� �h��<br />
O��s��i�� �a���� si���s s������c������� ���c����s a� i��ica���<br />
sp��ci��s f�� �h�� ���s� q�a��i�y si���s p����ai�i�� �� �h��<br />
s����a� �yp�� IV. O���y �w� sp��ci��s �Lype reducta<br />
�Ha������ 1868� a�� Hydroptila vectis C���is�� 1834�<br />
have relative high a���nities for the stream type V<br />
wh��� �h�� ��s� i�pac���� si���s a��� �����v��� f��� �h��<br />
s������c�i��.<br />
Fi�a����y�� s���� sp��ci��s ���.�. Hydropsyche incognita<br />
Pi�sch�� 1993�� H. contubernalis �c�ach��a��� 186���<br />
Oecetis notata �Ra������ 1842��� Allotrichia pallicornis<br />
�Ea����� 1873��� Cheumatopsyche lepida �Pic������ 1834���<br />
Athripsodes albifrons ��i��a���s�� 17�8�� hav�� �����a�iv��<br />
hi�h i��ica��� va�����s f�� �h�� s����a� �yp�� VI ���a����<br />
���w��a�� s����a�s�. N��v����h������ss�� �h��s�� hi�h va�����s<br />
hav�� �� ��� w��i�h���� �y �h�� �����a�iv�� f��w �������<br />
�f si���s avai��a����� f�� �his s����a� �yp��. �c��a����y��<br />
����y si� si���s �������� �� �h�� s����a� �yp�� ������� VI.<br />
Among the significant indicator species pointed<br />
��� f�� �h��s�� ��a����� �iv���s�� ����y H. contubernalis�� O.<br />
notata a�� A. pallicornis ca� ��� c��si������� as ����s�<br />
i��ica���s f�� �his �yp�� si�c�� �h��y hav�� hi�h a��<br />
specific a���nities for it. Species like H. incognita �� C.<br />
lepida are not specific for these large lowland rivers.<br />
I��������� ��v��� if �h��y a��� p������i�a����y f���� i� �h��<br />
s����a� �yp�� VI�� H. incognita a�� C. lepida �cc�� a��s�<br />
significantly in the stream type III (mid sized, mid<br />
a���i����� s����a�s i� �h�� O��s��i���.<br />
P<br />
<strong>Ferrantia</strong> • 55 / 2008
A. Dohet et al. Caddisfly assemblages characterizing different ecological areas in Luxembourg<br />
Tab. 4: List of indicator species for different stream types in �reference �reference reference condition� condition� condition� according to the<br />
PCA3. The �Avg� �Avg� Avg� and and �Max� �Max� �Max� �Max� Max� columns columns refer refer to to the the indicator indicator values values for for the the given given species species (av- (av- (av-<br />
erage and maximum value); �MaxGrp� is the type identifier for the group with the highest<br />
indicator value. The statistical significance of the observed indicator value is tested with a<br />
randomization (Monte Carlo) procedure: �SD� is the Standard Deviation; �P� evaluates the<br />
statistical significance of the maximum indicator value recorded for given species. The probability<br />
of type I error is the proportion of times that the maximum indicator value from the<br />
randomized data set equals or exceeds the maximum indicator value from the actual data<br />
set. Species are ordered according to the groups they are indicative for (ascending) and by<br />
observed indicator value (descending). Significant indicators for a particular stream type<br />
(IndVal ≥ 25.0 and p ≤ 0.05) are marked in bold characters.<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Types I+II III IV V Observed<br />
Number of items 27 10 20 5 IndVal<br />
IndVal from<br />
randomized<br />
groups<br />
Avg Max Max-<br />
Grp<br />
Mean SD<br />
Glossosoma conformis 7 61 I+II 61 0 0 0 61,2 9,8 5,61 0,001<br />
Philopotamus ludificatus 7 61 I+II 61 0 0 0 60,6 7,7 4,63 0,001<br />
Sericostoma personatum/schneideri 10 50 I+II 50 16 7 0 50,2 15,3 4,56 0,001<br />
Hydropsyche instabilis 7 49 I+II 49 0 1 2 49,0 11,8 5,31 0,001<br />
Oecismus monedula 5 43 I+II 43 0 0 0 43,0 7,4 4,70 0,001<br />
Odontocerum albicorne 7 41 I+II 41 0 10 0 40,7 11,1 4,76 0,001<br />
Philopotamus montanus 3 23 I+II 23 0 0 0 22��� 7��6 ���20 0��030<br />
Hydropsyche fulvipes 3 19 I+II 19 0 2 0 19��1 8��6 ����3 0��048<br />
Rhyacophila praemorsa 2 18 I+II 18 0 1 0 17��6 7��1 4��88 0��047<br />
Philopotamus variegatus 2 1� I+II 1� 0 0 0 14��8 ���2 4��11 0��032<br />
Brachycentrus montanus 2 13 I+II 13 0 0 0 13��1 6��1 4��90 0��074<br />
Crunoecia irrorata irrorata 1 8 I+II 8 0 0 0 7��7 ���7 4��31 0��208<br />
Hydatophylax infumatus 1 6 I+II 6 0 2 0 ���9 6��2 4��16 0��426<br />
Potamophylax latipennis 2 6 I+II 6 � 1 0 ���7 7��9 4��6� 0��61�<br />
Wormaldia occipitalis/subnigra 1 4 I+II 4 0 2 0 4��3 ���8 4��03 0���47<br />
Limnephilus flavicornis-Gr. 0 4 I+II 4 0 0 0 3��7 4��0 3��80 0��406<br />
Synagapetus iridipennis 1 3 I+II 3 0 3 0 2��8 ���2 4��41 0���7�<br />
Silo nigricornis 1 3 I+II 3 0 0 0 2��6 ���3 4��26 0��730<br />
Stenophylax permistus 0 2 I+II 2 0 0 0 2��3 4��3 3��89 0��731<br />
Polycentropus flavomaculatus 10 49 III 0 49 0 0 49,3 10,1 4,88 0,001<br />
Oecetis testacea 10 47 III 0 47 0 0 46,6 9,4 5,15 0,002<br />
Brachycentrus maculatus 8 44 III 0 44 0 0 43,7 10,5 6,39 0,003<br />
Mystacides azureus 10 41 III 0 41 0 0 40,6 11,1 5,59 0,004<br />
Allogamus auricollis 4 37 III 0 37 0 0 37,1 7,1 5,27 0,003<br />
Silo piceus 7 36 III 1 36 0 5 36,0 13,5 6,42 0,020<br />
Athripsodes bilineatus 5 30 III 0 30 0 0 30,2 10,3 6,45 0,020<br />
Ceraclea annulicornis 6 30 III 0 30 0 0 30,1 7,8 5,25 0,009<br />
Rhyacophila fasciata/dorsalis-Gr. 10 22 III 2 22 4 17 21��7 1���3 3���8 0��060<br />
Halesus tesselatus 3 21 III 0 21 0 0 20��6 6��8 4��64 0��022<br />
Athripsodes cinereus 6 20 III 0 20 0 � 20��1 7��7 4��63 0��030<br />
Setodes argentipunctellus 2 20 III 0 20 0 0 20��0 4��7 4���0 0��006<br />
Anabolia nervosa 4 18 III 1 18 0 0 18��0 8��0 4��88 0��044<br />
Potamophylax luctuosus 3 17 III 0 17 0 2 16��9 6��6 4��77 0��043<br />
P<br />
47
A. Dohet et al. Caddisfly assemblages characterizing different ecological areas in Luxembourg<br />
48<br />
Discussion<br />
Correspondence between<br />
ecological areas and caddisfly<br />
assemblages<br />
The broad landscape classification tested in this<br />
s���y�� ��v��� a� �h�� sca���� �f a s�a���� c�����y ��i���<br />
������������� ����y cap�����s a s��i�h� a�����<br />
of variation in the composition of caddisflies.<br />
I��������� ��a�i�i��a�� ��c�����ica�� a���as �f ������-<br />
����� �i.��.�� �h�� O��s��i�� a�� G����a�� �ai� ��c����gions<br />
and the Minette basin sub-ecoregion) were<br />
��� w������ s��pa�a���� �� �h�� ���i�a�i�� �PC�1�� Fi�.<br />
2�. H�w��v����� �h�� s��pa�a�i�� ����w����� �h�� av���a���<br />
plotting positions of �h�� the c�������a�i�� correlation ci�c����s circles<br />
c�����sp���i�� �� �h�� O��s��i�� a�� G����a�� c��ass��s<br />
Types I+II III IV V Observed<br />
Number of items 27 10 20 5 IndVal<br />
IndVal from<br />
randomized<br />
groups<br />
Avg Max Max-<br />
Grp<br />
Mean SD<br />
Anomalopterygella chauviniana 3 17 III 2 17 0 0 16��6 7��2 4��79 0��0�1<br />
Agapetus ochripes 1 9 III 0 9 0 0 9��0 7��2 ���33 0��214<br />
Chaetopteryx major 2 9 III 0 9 8 0 8��8 6��3 4��87 0��169<br />
Plectrocnemia conspersa 7 54 IV 2 0 54 0 53,7 11,2 5,78 0,001<br />
Drusus annulatus 6 47 IV 5 0 47 0 46,9 10,6 5,50 0,002<br />
Chaetopteryx villosa 8 39 IV � 7 39 2 39��4 23��2 9��84 0��062<br />
Potamophylax cingulatus 6 27 IV 19 0 27 0 26,6 11,3 5,37 0,026<br />
Rhyacophila tristis 3 23 IV 0 0 23 0 22��9 6��2 4��64 0��011<br />
Potamophylax latipennis/luctuosus 4 21 IV 1 1 21 3 20��8 10��� 6��00 0��0�9<br />
Tinodes cf. rostocki 3 21 IV 0 0 21 0 20��6 6��� 4��97 0��028<br />
Tinodes unicolor 4 19 IV 0 0 19 1 18��9 8��4 4��94 0��046<br />
Halesus radiatus � 1� IV 4 4 1� 4 1���2 12��6 ���31 0��217<br />
Synagapetus dubitans 2 1� IV 0 0 1� 0 1���0 ���0 4��60 0��063<br />
Melampophylax mucoreus 1 8 IV 0 0 8 0 8��2 ���0 3��88 0��1�3<br />
Beraeodes minuta 2 6 IV 0 6 6 4 6��1 7��7 4��9� 0���08<br />
Tinodes cf. pallidulus 1 � IV 0 0 � 0 ���0 3��9 3��6� 0��177<br />
Lithax niger 1 � IV 0 0 � 0 ���0 3��9 3���9 0��173<br />
Glyphotaelius pellucidus 0 3 IV 2 0 3 0 2��9 4��6 4��26 0���69<br />
Lype reducta 3 28 V 0 0 0 28 27,9 6,8 4,87 0,006<br />
Hydroptila vectis 4 26 V 0 0 0 26 26,2 6,6 4,66 0,008<br />
Hydropsyche saxonica � 19 V 12 0 3 19 19��0 12��� ���36 0��106<br />
Annitella obscurata 2 14 V 0 0 0 14 14��1 6��9 4��89 0��088<br />
Mystacides longicornis-Gr. 3 13 V 0 3 0 13 12��9 7��6 ���29 0��10�<br />
Tinodes waeneri 2 11 V 0 0 0 11 11��0 ���9 4��43 0��096<br />
was evident. The mean plotting position of the<br />
Minette basin ellipse was slightly separated from<br />
�h�� ��h��� ����s ��� a���� si���s �f �his ������aphica��<br />
c��ass a��� i�c������� i� �h�� G����a�� ����i��. I�<br />
c��s��q����c���� ����y �h�� s��pa�a�i�� ����w����� �h�� �w�<br />
�ai� ��c�����ica�� a���as i� ����������� �i.��. O��s��i��<br />
a�� G����a��� ca� ��� c��si������� as ���a�i��f���<br />
according to caddisfly assemblages. The relative<br />
low performance of the stratification by ecoregions<br />
was a��s� ��s���v��� i� s��v���a�� c�����i��s a���� �v���<br />
�h�� w����� ���.�. G����i�s��� et al. 2000�� �a�cha�� et<br />
al. 2000�� �a��i� & J�h�s�� 2000�� F���i�������a 2000��<br />
���������� et al. 2004�. O� �h�� c����a�y�� ���� et al.<br />
�2004� c��si���� �ha� �h�� ��c�����i�� c��c��p� was<br />
confirmed as a valuable tool for the prediction of<br />
��s��ia� �iv��� fa��as. N��v����h������ss�� �h�� a��h��s<br />
s�����s� �� �ivi��� ��a���� ��c�����i��s i��� s�a�������<br />
������aphic ��i�s�� which �as��� �� ��c�����ica��<br />
knowledge and theory, are expected to differ in<br />
P<br />
<strong>Ferrantia</strong> • 55 / 2008
A. Dohet et al. Caddisfly assemblages characterizing different ecological areas in Luxembourg<br />
�h��i� sp��ci��s c��p�si�i��. �cc���i�� �� Haw�i�s<br />
et al. �2000��� ���������� et al. �2004� a�� �������� et al.<br />
�2004��� �h�� ��acc�������-f�� ����a�i�� �f �iv���s a��<br />
�h�� ��acc�������-f�� ca�s��s �f �i�����ica�� va�ia�i��<br />
at different spatial scales are among the more likely<br />
���as��s ���p��ai�i�� �h�� �����a�iv�� p��� p���f���a�c��<br />
of ecoregion classifications.<br />
Performance of the stream typology<br />
relative to the classification based<br />
on the ecological areas<br />
�����a� �i����si���� ������va�i�� a�� ��������y a��� �h��<br />
�h����� ���y �yp�����ica�� ���sc�ip���s�� which ���a����� ��<br />
clearly distinguish the six stream types defined in<br />
����������� �as��� �p�� a c���i�a�i�� �f c��assification<br />
and ordination procedures (Ferréol et al.<br />
200��. Th�� pa��ic���a�i�y �f �his �yp�����y is �h��<br />
c�i�ci����c�� ����w����� ���vi��������a�� ��a�i����s<br />
s�ch as �h�� �i����a��i��a�i�� �f �h�� wa���� ������a����<br />
�� �h�� ��������ica�� �is�i�c�i�� ����w����� �h�� ����h<br />
a�� �h�� s���h �f �h�� c�����y��� �h�� ������va�i�� a��<br />
�h�� �w� �ai� ��c�����ica�� ����i��s �i.��.�� O��s��i�� a��<br />
G����a���. I� c��s��q����c���� �h�� s����a� �yp�����y<br />
�f ����������� ca� ��� assi�i��a���� �� a pa��i�i��<br />
�f �h��s�� �w� �ai� ��c�����ica�� a���as ���s���� �y �h��<br />
ca�ch������s si���� ��a�i����. Th�s�� �h����� is a c���s��<br />
c�����sp������c�� ����w����� ��a�i�i��a�� ������aphica��<br />
a���as �f ����������� �� �h�� ���� ha���� a�� �h��<br />
s����a� �yp�����y �� �h�� ��h��� ha��. Th�����f������<br />
�h�� c����a� ���ha�c������� �f �h�� p���f���a�c�� �f �h��<br />
s����a� �yp�����y i� c��pa�is�� �� �h�� ��c�����ica��<br />
a���a c��ass��s �c��pa��� Fi�. 3 a�� Fi�. 2��� i� �����s �f<br />
the variation in caddisfly compositions captured<br />
by the classification, is not surprising. Indeed,<br />
�h�� i�p���a�c�� �f �h�� �����i���i�a�� ����a�i�� i�<br />
s����a�s has ��� �� ��� ������s��a���� a�y �����<br />
(e.g. Illies & Botosaneanu 1963, Vanotte et al. 1980��<br />
W�i�h� et al. 1984�� B���sa���a�� 1988�� Wass�� 1989��<br />
Wi�����-�a�s��� et al. 2000�. I� G����a�y�� �������� et<br />
al. �2004� c��si������� �h�� si���� ��a�i���� ���p���ss���<br />
as ca�ch����� si������ s����a� wi��h�� �� �is�a�c�� ��<br />
s���c���� as a p���vai��i�� "�yp�����ica����y �������va��"<br />
pa�a������� �� c��p��������� ��c�����i��s a�� ���p��ai�<br />
�h�� c��p�si�i�� �f s����a� fa��a. I� �h�� h����������-<br />
�����s ��a��scap�� �f �h�� �i�-����a��ic Hi�h��a��s<br />
�U����� Wai��� et al. (2000) observed that classifica�i��<br />
s�������hs �y ��c�����i��s i�c���as��� if si���s<br />
were previously stratified by stream order. They<br />
c��c������� �ha� �h�� �ac��i�v��������a���s s��������<br />
�� ���sp��� p�i�a�i��y �� s���p�� a�� s����a� ������<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
a�� �h��� �� �h�� ��a��scap�� fac���s s���a�i�����<br />
�y ��c�����i��s. Wi�����-�a�s��� et al. �2000� f����<br />
�ha� T�ich�p����a sp��ci��s �ich���ss a�� ass������a���<br />
c��p�si�i�� i� Da�ish s����a�s p�i�a�i��y sh�w a<br />
s����� ass�cia�i�� wi�h s����a� �������� wi��h a��<br />
s���p���� a�� s��c���a�i��y wi�h p���s���c�� / a�s���c��<br />
�f �ipa�ia� f����s�. Th��s�� ���s����s s�����s� �ha�<br />
landscape-scale classifications can only provide<br />
a general representation of the spatial patterns<br />
i� i�v��������a��� ass������a���s a�� ca���� ��� �s���<br />
reliably to predict characteristics for a specific<br />
si��� ���ca�s�� i�s����a� physica�� ha�i�a� ���c����s<br />
h�����������s a�� �is�i�c�iv�� a� �����a�iv����y s�a����<br />
spa�ia�� sca����s ����������� et al. 2004�.<br />
D��spi��� �h�� c��pa�a�iv����y s�a���� ������� �f ���a�-<br />
���f������c�� si���s avai��a������� �����a�iv����y �is�i�c� c���s����s<br />
can be distinguished according to their caddisfly<br />
assemblages (PCA3: Fig. 4). Besides the overall<br />
better separation of clusters with these selected<br />
sites, the improvement of the classification is<br />
��sp��cia����y ��vi��s f�� �h�� s����a� �yp��s IV a�� V<br />
����sp��c�iv����y�� s�a���� si����� �i� a���i����� s����a�s i�<br />
�h�� G����a�� a�� �i� si����� ���w a�� �i� a���i�����<br />
streams in the Gutland). . The latter stream types<br />
a��� i�c������� i� �h�� G����a�� ��c�����ica�� a���a wh�����<br />
h��a�-i���c��� p�������a�i��s a��� ����� ��i�����y ��<br />
�cc�� �i.��.�� ����� ����s����y p�p���a���� a���a�� �����<br />
p���ss����s f��� i���s��y a�� a��ic���������. Th�s��<br />
�h��s�� ���s����s s�����s� �ha� �h�� �i�i�� �f ���f������c��<br />
a�� ������f������c�� si���s i� �h�� p���vi��s ���i�a�i��<br />
(PCA2: Fig. 3) was the principal reason explaining<br />
the absence of distinct caddisfly assemblages<br />
����w����� �h��s�� �w� s����a� �yp��s. ����h���h Wai���<br />
et al. �2000� a�� �cC���ic� et al. �2000� a�a��y��i��<br />
respectively invertebrate and fish assemblages,<br />
i� �h�� �i�-�ppa��achia� Hi�h��a��s �U��� hav��<br />
shown similar classification strength results from<br />
��i�h��� �a������y s������c���� si���s �� ����y ���f������c��<br />
si���s�� a p�������a�i�� ��a�i���� is ��i�����y �� �as� ���a��<br />
�isc���i��i�i��s a�� �ypica�� i�v��������a��� ass���blages<br />
present in different classes (Stroot 1991,<br />
V������sch�� 199��� �������� et al. 2004�. Th�����f����<br />
�h�� i�p��v������� �f �h�� �����a�i��ship ����w�����<br />
caddisfly assemblages and the classification based<br />
�� �h�� s����a� �yp�����y a�� �h�� s������c�i�� �f ���a�-<br />
���f������c�� si���s�� as ��s���v��� i� ��� ���s����s�� is ���<br />
���a����y s��p�isi��.<br />
H�w��v����� ���spi��� �h�� s������c�i�� �f �h�� ���a�-<br />
���f������c�� si���s�� s����a� �yp��s I a�� II ����sp��c�iv����y��<br />
����sp��c�iv����y��<br />
s�a���� hi�h a���i����� a�� s�a���� �i� a���i����� s����a�s��<br />
���h i� �h�� O��s��i��� ca� ca� s�i���� s�i���� ��� ��� ��� ��� �is�i���ish���<br />
�is�i���ish���<br />
49
A. Dohet et al. Caddisfly assemblages characterizing different ecological areas in Luxembourg<br />
50<br />
according to their caddisfly communities. The<br />
������va�i�� ��a�i������ which ���a�����s �� s��pa�a���<br />
�h��s�� �w� s����a� �yp��s �� �h�� �asis �f ���s�����ica��<br />
va�ia�����s �s���� Ta�. 1��� ����s ��� i�v���v�� �is�i�c�<br />
caddisfly assemblages. According to Rundle et<br />
al. �1993� a�� B���wi� et al. �199�� wh� a�a��y�����<br />
�ac��i�v��������a��� c�����i�i��s i� �h�� Hi�a��aya<br />
�N��pa����� �h�� a���i����� was �h�� ��s� i�p���a��<br />
fac��� ���p��ai�i�� �h�� s��pa�a�i�� �f s����a� ass���-<br />
���a���s. O�vi��s��y�� �h�� a���i���i�a�� �a���� �f ������bourg<br />
(i.e., 150 – 550 m.) is not in the same size<br />
������ �ha� �h�s�� �f �h�� N��pa����s�� Hi��a��aya �i.��.��<br />
600 – 3800 m.). The elevation gradient observed in<br />
Luxembourg is most likely not su���cient to induce<br />
different adaptations of caddisfly species and<br />
������v��� �h�� app��a�a�c�� �f �is�i�c� c�����i�i��s.<br />
This ������ is ��� ���c���siv�� �� T�ich�p����a si�c��<br />
c�����i�i��s c��p�s��� �f ��h��� �����hic i�v������-<br />
��a��� ����ps w����� a��s� �a�h��� si�i��a� wi�hi� �h��s��<br />
�w� s����a� �yp��s �D�h����� ��p����ish��� ���s����s�.<br />
Th�s�� acc���i�� �� �h�� �����hic i�v��������a��� ass���-<br />
���a���s�� �h�� �����i�� �f �h�� s����a� �yp��s I a�� II<br />
c����� ��� p��p�s��� i� ������ �� achi��v�� ����a����<br />
acc��acy a�� p���cisi�� a���� h���c���� ����� �����ia�����<br />
ass��ss�����s �f �h�� �i�����ica�� c���i�i��s.<br />
Implications for the design and<br />
use of biological assessments in<br />
aquatic ecosystem management<br />
Th�� �s��f������ss �f �ac��i�v��������a��� ass������a���s<br />
f�� ���i���i�� wa���� q�a��i�y a�� �i�����ica��<br />
i������i�y ���p����s i� pa�� �� ��� a�i��i�y ��<br />
�is�i���ish h��a� i�pac�s f��� �a���a�� va�ia�i��i�y<br />
�Wai��� et al. 2000). Classification is thus a critical<br />
c��p������ i� �a�y �i�ass��ss����� p����a�<br />
���si��s �� ass��ss �h�� h��a���h �f s����a�s �Haw�i�s<br />
et al. 2000�. H�w��v����� sy��h��si��i�� �h�� ���s����s �ha�<br />
���������� f��� s��v���a�� pap���s ���sc�i�i�� va�ia�i��<br />
i� aq�a�ic �i��a a� ��a��scap�� spa�ia�� sca����s��<br />
Haw�i�s et al. �2000� c��c������� �ha� ��a����-sca����<br />
����i��a��i��a�i��s�� if �s��� a������ �� sp��cify ���p��c����<br />
c���i�i��s�� wi���� ��i�����y hav�� ��i�i���� �s�� i� �i��ic<br />
ass��ss������� wh����� i� is c�i�ica�� �� sp��cify ���p��c����<br />
c���i�i��s as acc��a�����y a�� p���cis����y as p�ssi�����.<br />
W�� a������ wi�h �his �pi�i���� ��� ��� ���s����s a��s�<br />
suggest that a broad scale classification based<br />
on geographical areas can account for su���cient<br />
variation among biotic data, if this classification<br />
is ���s���� �y a s����a� si���� ��a�i���� ���.�. s����a�<br />
�������� ca�ch����� si������ �is�a�c�� �� s���c���. Wai��� et<br />
al. �2000� a��s� a������ �ha� ��c�����i��/ca�ch����� i�<br />
c���i�a�i�� wi�h ��h��� va�ia�����s s�ch as s����a�<br />
�������� s����a� ��a�i������ �� ��h��� physica�� s����a�<br />
f��a�����s �ay ��� �s��f��� �����s �� h����p pa��i�i�� �h��<br />
va�ia�c�� �f �i�����ica�� ass������a���s a�� �h�s ��<br />
i�p��v�� ��� ������s�a��i�� a�� i�����p����a�i��<br />
�f s����a� sys����s. W�� a��s� ac���w�������� �h��i�<br />
arguments that environmental classifications may<br />
need to account for the striking shift that often<br />
�cc��s f��� h��a�wa����s �� �i�-������ s����a�s<br />
i� s����a� cha�ac����is�ics a�� ���s����i�� �i�����ica��<br />
ass������a���s.<br />
Th�� ���s����s �f �his i�v��s�i�a�i�� a��s� s�����s�<br />
�ha� a� i����a�iv�� p��c��ss�� which c��sis�s i� �si��<br />
�������va�� i�f���a�i���� i�c����i�� p�i�� ���w��������<br />
and classification, measured data, and exploratory<br />
s�a�is�ica�� a�a��ysis�� is a� app��p�ia��� s��a����y ��<br />
achieve the most effective classifications (Gerritsen<br />
et al. 2000). Thus, besides classifications that can<br />
��� ����� ��i�h��� wi�h physica�� f��a�����s �a p�i��i� ��<br />
�y a�a��ysis �f �i�����ica�� �a�a wi�h��� physica��<br />
f��a�����s �a p�s����i��i��� a 3 �� a�������a�iv�� c��sis�s<br />
to test and refine physically derived classes with<br />
s��s��q����� a�a��ysis �f �i�����ica�� �a�a �G����i�s���<br />
et al. 2000�. This 3 �� a�������a�iv���� a��p���� i� �his<br />
study, is probably the best-suited strategy to attain<br />
water quality goals and fulfill the requirements of<br />
�h�� EU wa���� f�a���w��� �i���c�iv��.<br />
Characteristic indicator species of<br />
<strong>Trichoptera</strong> in the different stream<br />
types<br />
The most robust classification that emerged from<br />
��� ���s����s �i.��.�� s����a� �yp�����y wi�h �h�� s����a�<br />
�yp��s I a�� II �������� ������h���� was �s��� ��<br />
identify characteristic caddisfly communities by<br />
�h�� ���a�s �f �h�� INDV�� ����h��.<br />
Th�� sp��ci��s �ha� sh�w hi�h p���f������c��s f�� s�a����<br />
hi�h a�� �i� a���i����� s����a�s i� �h�� O��s��i��<br />
�i.��.�� Sericostoma schneideri/personatum�� Glossosoma<br />
conformis�� Hydropsyche instabilis�� Odontocerum<br />
albicorne�� Agapetus fuscipes�� Philopotamus ludificatus��<br />
Potamophylax cingulatus�� Oecismus monedula<br />
a�� Silo pallipes� a��� a���� c����� i�ha�i�a��s �f<br />
s�a���� h��a�wa���� s����a�s i� c���i�����a�� E���p��<br />
���.�. V������a�� 1973�� B���sa���a�� & �a��ic�y 1978��<br />
������ 1984�� Hi������ & ������� 1986�� Pi�sch 1993��<br />
E�i����� & Hi������w 199��. H�w��v����� sp��ci��s ��i���<br />
O. albicorne �� S. pallipes are often considered as<br />
<strong>Ferrantia</strong> • 55 / 2008
A. Dohet et al. Caddisfly assemblages characterizing different ecological areas in Luxembourg<br />
����y��pic sp��ci��s �V������a�� 1973�� B���sa���a��<br />
& �a��ic�y 1978�� ������ 1984�� D�h��� et al. 2002�. I�<br />
our dataset, despite a higher a���nity for the small<br />
hi�h a�� �i� a���i����� s����a�s i� �h�� O��s��i���� �h��<br />
latter species are not exclusive for this stream type<br />
and show some a���nities for other stream types as<br />
w������ �s���� Ta�. 3�. �a�va�� �f Sericostoma schneideri<br />
�ch���i������ 184� a�� S. personatum ��p���c�� i�<br />
Kirby & Spence, 1826) are di���cult to distinguish<br />
f��� ��ach ��h����� ��sp��cia����y ��a���y i�s�a�s ��a�va��.<br />
On the contrary, the adults can be identified<br />
�����a�iv����y ��asi��y. �i�c���� ��� a�a��ys��s a��� �as��� ��<br />
larval identification, the two Sericostoma sp��ci��s<br />
w����� ��� s��pa�a����. H�w��v����� s���� cap�����s<br />
�f a�����s ����� �� i��ica��� �ha� S. personatum is<br />
����� ���s��ic���� �� h��a�wa���� s����a�s wh�����as S.<br />
schneideri p������i�a����y �cc��s i� ���w��� ���ach��s<br />
�s�a���� �� �i������-si����� s����a�s�. This s�cc��ssi��<br />
�f �h�� �w� Sericostoma sp��ci��s a����� �h�� �����i��dinal<br />
gradient is confirmed in the literature (e.g.<br />
Pi�sch 1993�� R������ 1996�� G�����c��� et al. 200��. This<br />
trend is revealed by the different allocations of<br />
�h�� i��ica��� va�����s �f �h�� c��p����� S. schneideri/<br />
personatum f�� �h�� s����a� �yp�� I+II �� �h�� ����<br />
ha�� a�� �h�� s����a� �yp�� III �� �h�� ��h��� ha��<br />
(Tab. 3). Among the species that remain significant<br />
i��ica���s �f �h�� s����a� �yp�� I+II wh��� ����y ���a�-<br />
���f������c�� si���s a��� s������c������ ����y P. ludificatus�� O.<br />
monedula a�� �� a ����ss��� �������� G. conformis a���<br />
cha�ac����i����� �y hi�h��� i��ica��� va�����s. I���������<br />
�h�� i��ica��� va�����s f�� P. ludificatus a�� O.<br />
monedula significantly increase from 31 to 61 and<br />
27 �� 43�� ���sp��c�iv����y �Ta�. 3 a�� 4�. Th�s �h��s��<br />
sp��ci��s ��s� ��� c��si������� as ����� i��ica���s �f �h��<br />
s�a���� hi�h a�� �i� a���i����� s����a�s i� �h�� O��s��i��<br />
i� �h�� a�s���c�� �f a��h��p�����ic a������a�i��s. Pi�sch<br />
�1987�� 1993� a�� ���� �199�� c��si���� �h��s�� �a�a<br />
as v���y s���si�iv�� �� ���a�ic p�������i�� a�� ��h���<br />
�is����a�c��s.<br />
I� �h�� sa��� s����a� si���� c��ass�� ��� i� �h�� ��h���<br />
�ai� ��c�����ica�� a���a �i.��.�� �h�� G����a����� �h�� sp��ci��s<br />
that have high a���nities for the stream type IV,<br />
a��� �a�h��� sca�c��. �c��a����y�� ����y Plectrocnemia<br />
conspersa�� Tinodes unicolor a�� Drusus anulatus<br />
are significant indicators and among them, only<br />
T. unicolor is p���s���� ���c���siv����y i� �his s����a�<br />
�yp��. H�w��v����� si�i��a���y �� �h�� s�a���� s����a� �yp��<br />
i� �h�� O��s��i���� �h�� i��ica��� va����� �f P. conspersa<br />
a�� D. annulatus c����a���y i�c���as��s wh��� ����y<br />
���a�-�a���a�� si���s a��� s������c���� �i.��. f��� 31 �� �4<br />
a�� f��� 26 �� 47 f�� P. conspersa a�� D. annulatus��<br />
���sp��c�iv����y�. U����p��c������y�� P. cingulatus�� which<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
sh�w��� a hi�h p���f������c�� f�� s�a���� hi�h a�� �i�<br />
a���i����� s����a�s i� �h�� O��s��i�� wh��� �h�� wh����� s���<br />
of data was used, becomes a significant indicator<br />
�f s�a���� �i� a���i����� s����a�s i� �h�� G����a�� wh���<br />
�h�� �a�as��� is ���s��ic���� �� ���a�-���f������c�� si���s.<br />
Wha���v����� �h��s�� �h����� sp��ci��s �i.��.�� P. conspersa��<br />
D. annulatus a�� P. cingulatus� �ay ��� c��si�������<br />
as i�p���a�� i��ica���s �f �i�i�a����y �is�������<br />
s�a���� �i� a���i����� s����a�s i� �h�� G����a�� a���a.<br />
C��c����i�� D. annulatus, Moog (1995) attributes<br />
a saprobic valence range (reflecting the tolerance<br />
a� ���a�is� has f�� ���a�ica����y �ich s��s�a�c��s�<br />
qualified as xenosaprobic �����sap���ic to �� oligosaprobic.<br />
���i��sap���ic. P.<br />
conspersa has a �����a�iv�� hi�h��� �a���� �f �������a�c�� ��<br />
organic pollution (from xenosaprobic to α-mesosap���ic<br />
�������. P. cingulatus has a���nities for the<br />
xenosaprobic to β-mesosaprobic zone. Compared<br />
�� ��h��� Potamophylax sp��ci��s�� Hi������ & �������<br />
�1986� c��si���� �ha� P. cingulatus has a p���f������c��<br />
f�� s�a������� �pp��� c���s��s a�� ����� s������h����<br />
c���i�i��s.<br />
Wh��� c��si����i�� �i� �i� si������� si������� �i� �i� a���i����� a���i����� s����a�s s����a�s<br />
i� �h�� O��s��i�� �s����a� �yp�� III��� w�� ���ic�� a c����a�<br />
decrease in the number of significant indicator<br />
sp��ci��s i� pa�a�������� wi�h a c����a� ���c���as�� �f �h��i�<br />
i��ica��� va�����s�� wh��� w�� ���s��ic� �h�� �a�a ��<br />
���a�-�a���a�� si���s. Th�� ����y ���c��p�i�� �� �his<br />
�������a�� ������ is Athripsodes bilineatus�� which<br />
sh�ws a hi�h��� i����� wh��� ���s� q�a��i�y si���s a���<br />
s������c���� i� c��pa�is�� �� �h�� c���i�a�i�� �f<br />
���f������c�� a�� ������f������c�� si���s �c��pa��� �c��pa��� Ta�. Ta�.<br />
3 a�� 4�. . G�af G�af et al. �2006� assi�� A. bilineatus ��<br />
hyp��hi�h�a�� a�� ��pip��a�a�� ������s a����� �h��<br />
�����i���i�a�� s����a� ��a�i����. H�w��v����� �his �a���<br />
is ��� c��si������� as a s���si�iv�� sp��ci��s. �cc���i�� �cc���i��<br />
�� ���� �199���� A. bilineatus is categorized as a �β-<br />
���s�sap���ic" sp��ci��s. �� a�a������s ��s���va�i��<br />
ca� ��� �a��� f�� �h�� s����a� �yp�� V ��i� si�������<br />
�i� a���i����� s����a�s i� �h�� G����a���. I��������� H.<br />
pellucidula a�� H. angustipennis�� which a��� �ypica��<br />
sp��ci��s �f �h�� s����a� �yp�� V i� �h�� wh����� �a����<br />
�f a��h��p�����ic �is����a�c��s a��� ���p��ac��� �y<br />
Hydroptila vectis a�� Lype reducta if �h�� ���s� q�a��i�y<br />
si���s avai��a����� f�� �h��s�� s����a� �yp�� a��� s������c����.<br />
Both species are categorized as �β-mesosaprobic�<br />
sp��ci��s a�� L. reducta is c��si������� as a ha�i�a�<br />
sp��cia��is� ��y����i���ic� sp��ci��s ����� 199���<br />
G�af et al. 2006�. ����� �������a����y�� �h�� ���c���as�� �f<br />
cha�ac����is�ic sp��ci��s a�� ass�cia���� i��ica���<br />
va�����s ��s���v��� i� ��a���� s����a� �yp��s �i.��. �yp��s<br />
III i� �h�� O��s��i�� a�� �yp�� V i� �h�� G����a��� i�<br />
c��pa�is�� �� s�a���� s����a� �yp��s �i.��. �yp��s I+II i�<br />
51
A. Dohet et al. Caddisfly assemblages characterizing different ecological areas in Luxembourg<br />
52<br />
�h�� O��s��i�� a�� �yp�� IV i� �h�� G����a��� is ��i�����y<br />
�� ��� a c��s��q����c�� �f �h�� �����ip���� a��h��p�����ic<br />
pressures that affect large parts of European rivers<br />
f�� ���ca���s. H��a�-�������a���� �is����a�c��s<br />
s�ch as i�����siv�� a��ic���������� i���s��y ��<br />
���f����s�a�i�� ����� pa��ic���a���y c��c���� ��a����<br />
streams flowing in the lowlands and often are<br />
ass�cia���� wi�h ����� ����s����y p�p���a���� a���as.<br />
I� �h�s�� ����i��s�� a��h��p�����ic �is����a�c��<br />
is wi���sp���a� a�� p�is�i��� ca�ch�����s �� s��catchments<br />
are consequently extremely di���cult<br />
to find (e.g. Wasson 2001, Lorenz et al. 2004��<br />
Nijboer et al. 2004�. ���ai�h����i�� �f s����a�s�� �a�<br />
c��s���c�i���� �h�� �isc�����c�i�� �f �h�� s����a�<br />
from its floodplain and alteration of riparian<br />
s���c����� a�� v������a�i�� ����� �� a ���ss �f s��v���a��<br />
ha�i�a� �yp��s a�� ass�cia���� sp��ci��s �Zwic� 1992�.<br />
Th�����f������ i� is ��� s� s��p�isi�� �ha� w�� f����<br />
a c��pa�a�iv����y ���w��� ������� �f cha�ac����is�ic<br />
sp��ci��s i� �h�� ��a���� s����a� �yp��s �i.��.�� �yp��s III a��<br />
V��� pa��ic���a���y wh��� i��ica��� sp��ci��s a�a��ys��s<br />
a��� ���s��ic���� �� ���s� avai��a����� q�a��i�y si���s f��<br />
the different stream types. These findings have<br />
p���a���y �� ��� c��pa���� �� �h�� ����i�c�i�� �a���<br />
�f ��������s sp��ci��s cha�ac����is�ic �f �h�� ���w���<br />
���ach��s�� �v��� �h�� ��as� ���ca���s. I��������� ������<br />
�1989��� ���a�i�i�� �h�� p���f������� ha�i�a�s �f �h��<br />
��s� �h���a������� T�ich�p����a sp��ci��s�� has sh�w�<br />
that besides different types of ponds and swamps<br />
wi�h �ich v������a�i���� a�� sp�i�� s���c��s�� �h�� ���w���<br />
���ach��s a�� �h�� ��a���� ���w��a�� �iv���s�� acc�������<br />
f�� �h�� ��s� ����a�������� ha�i�a�s. I� c��pa�is����<br />
�h�� si��a�i�� �f sp��ci��s i�ha�i�i�� s�a���� a�� �i�<br />
si����� s����a�s was �����a�iv����y ����ss c�i�ica���� a� ����as�<br />
a� �h�� sca���� �f �h�� E���p��a� c�����i�y. I� �his<br />
c��������� i� sh����� ��� ���phasi����� �ha� sp��ci��s<br />
��i��� Agapetus laniger �Pic������ 1843��� Tricholeiochiton<br />
fagesii �G�i�a���� 1879��� Chimarra marginata<br />
��i��a���s�� 1767��� Ecnomus tenellus �Ra������ 1842���<br />
Cyrnus flavidus �c�ach��a��� 1864�� Neureclipsis<br />
bimaculata ��i��a���s�� 17�8��� Micrasema longulum<br />
�c�ach��a��� 1876�� M. minimum �c�ach��a��� 1876��<br />
Limnephilus sparsus C���is�� 1834�� Stenophylax<br />
permistus �c�ach��a��� 189��� Athripsodes leucophaeus<br />
�Ra������ 1842��� Ceraclea nigronervosa �R�����i�s��<br />
1783��� Leptocerus interruptus �Fa��ici�s�� 177���� L.<br />
tineiformis C���is�� 1834 �� Setodes argentipunctellus<br />
�c�ach��a��� 1877�� which w����� c��si������� as<br />
�����a�iv����y a����a�� a��/�� wi���sp���a� sp��ci��s i�<br />
the lower part of Luxembourg�s �ss rivers (Hoffmann<br />
1970�� �ch�a������ et al. 2002� a��� ���a����y ����a��������<br />
sp��ci��s �� ��v��� hav�� c��p���������y �isapp��a����<br />
���i�� �h�� ��as� ���ca���s. ����� �h����� s����<br />
sp��ci��s w����� p���a���y v���y s���si�iv�� �� h��a�i���c���<br />
a������a�i��s. T�ich�p����a ass������a���s<br />
��s���v��� a� �h�� p���s���� �i��� i� ��a���� ���w��a��<br />
�iv���s f��� ����������� a��� �ai���y c��p�s���<br />
�f �����a�iv����y ����y��ci��s sp��ci��s �ha� hav�� ���sis����<br />
���i�� ��w �� �h�� �v���a���� a��h��p�����ic p���ss����s<br />
of different types that predominantly affect this<br />
kind of ecosystems. By definition, those species<br />
hav�� �����a�iv�� ���a� ���vi��������a�� ���q�i��������s<br />
a�� a��� ��� ��i�����y �� ��� ���c���siv�� f�� ���� �� a���h���<br />
s����a� �yp�� �i.��.�� �h��i� i��ica��� va�����s wi���� ��� v���y<br />
���w�.<br />
F�� si�i��a� ���as��s�� �� si���s ��������i�� �� �h��<br />
��a����s� s����a� �yp�� ���sc�i���� i� �����������<br />
�s����a� �yp�� VI� ca� ��� c��si������� as ���a�-<br />
���f������c��. �p��ci��s �ha� app��a� as cha�ac����is�ic �f<br />
�his ��a���� ���w��a�� �iv��� sys���� ��s� ��� w��i�h����<br />
�y �h�� fac� �ha� ����y a f��w si���s w����� sa�p����� f��<br />
�his s����a� �yp�� �s���� Ta�. 3�. Ta�i�� i��� acc����<br />
�his ���s���va�i���� w�� �ay ���ic�� �ha� s��v���a��<br />
sp��ci��s �cc���i�� i� �his ��a���� ���w��a�� �iv��� a���<br />
��� f���� ����s��wh�����. This is pa��ic���a���y �h��<br />
cas�� f�� Hydropsyche contubernalis�� Oecetis notata<br />
a�� Allotrichia pallicornis�� which a��� p�ac�ica����y<br />
���c���siv�� f�� �his s����a� �yp�� i� �����������.<br />
Hydropsyche incognita�� Cheumatopsyche lepida��<br />
Athripsodes albifrons a�� Ceraclea dissimilis<br />
�����ph���s�� 1836� �ay ��� c��si������� as i��ica���s<br />
�f �h�� ���w��� s��c�i��s �f �iv���s�� wha���v��� �h��y a���<br />
i� ���� �� a���h��� ��c�����i��. I��������� �h�s�� sp��ci��s<br />
have high a���nities for both largest stream types<br />
i� �h�� O��s��i�� a�� �h�� G����a�� ������aphica�� a���as<br />
�Ta�. 3�.<br />
I� was a�����a�y p�i����� ��� �ha� �a�y sp��ci��s a���<br />
�a��� i� �h�� s���s�� �ha� �h��y a��� p���s���� i� ����y a<br />
s�a���� % �f c�������c�i��s �� ���p���s���� a v���y ���w<br />
p��p���i�� �f �h�� ���a�� a����a�c�� ���as����� a�<br />
�h�� wh����� c�����i�y ����v����. I� c����as��� �h����� a���<br />
a��s� s��v���a�� c����� �a�a �ha� a��� cha�ac����i�����<br />
�y ���a� ������aphic �is��i���i��s a�� �ha� �cc��<br />
i� a wi��� va�i���y �f s����a�s. ����� �h�� ��s�<br />
wi���sp���a� sp��ci��s �f �h�� T�ich�p����a ass������a���s<br />
��s���v��� i� ������������� Hydropsyche siltalai��<br />
Chaetopteryx villosa a�� Rhyacophila dorsalis/fasciata-<br />
Gr. show a���nities (i.e., indicator values > 0) for<br />
��s� �f �h�� s����a� �yp��s ���sc�i���� i� �h�� p���s����<br />
s���y. Th�� ����y��pic f��a�����s �f �h�s�� sp��ci��s<br />
were also demonstrated in different biocenotic<br />
i�v��s�i�a�i��s ���.�. V������a�� 1973�� ������ 1984�.<br />
<strong>Ferrantia</strong> • 55 / 2008
A. Dohet et al. Caddisfly assemblages characterizing different ecological areas in Luxembourg<br />
Conclusions<br />
Haw�i�s a�� N���is �2000� sy��h��si����� �h�� ���s����s<br />
�f a ������� �f pap���s ���sc�i�i�� va�ia�i�� i� aq�a�ic<br />
�i��a a� a ��a��scap�� spa�ia�� sca����. Th��y c��c�������<br />
that even if ecoregion classifications accounted for<br />
significantly more variation in biotic assemblages<br />
�ha� w����� ��� ���p��c���� �y cha�c���� �h�� a����� �f<br />
�i��ic va�ia�i�� �����a���� �� ��a��scap�� f��a�����s was<br />
often rather weak. These authors put forward the<br />
following explanations for this poor relationship:<br />
�1� �a�a ca� va�y i����p����������y a�� c���i����s��y<br />
�v��� ���vi��������a�� ��a�i����s; c��s��q�������y�� c��assifications<br />
can create artificial discontinuities that do<br />
��� ���is� i� ���a��i�y; �2� �h����� ca� ��� a ��a���� wi�hi�c��ass<br />
�i�����ica�� h�������������i�y�� ��� acc������� f��<br />
by the classifications (incomplete sampling, high<br />
h�������������i�y a���� si���s�� p���i�i�y �� �isp���sa��<br />
effects, local habitat features,…); (3) biotic assem-<br />
���a���s a��� c��p�s��� �f �a�y c����� sp��ci��s��<br />
which �cc�� ���a���y ��v���ywh����� a�� wi���� p�����tially<br />
mask real biological differences among sites.<br />
O� �h�� c����a�y�� �a�y sp��ci��s a��� v���y �a���. Th��y<br />
are restricted to very specific ecological conditions<br />
and contribute little to the discrimination of<br />
����ps.<br />
The results presented in this paper confirm that<br />
the concept of ecoregion classification, even at<br />
�h�� sca���� �f a s�a���� c�����y ��i��� ������������� is<br />
not su���ciently strong to warrant its use alone<br />
as a classification tool for the evaluation of the<br />
biological assemblages (exemplified here by the<br />
T�ich�p����a c�����i�i��s�. H�w��v����� if �h��s��<br />
������aphica�� c��ass��s a��� ���s���� wi�h va�ia�����s<br />
���p���ssi�� �h�� �����i���i�a�� s����a� ��a�i����<br />
���.�. s����a� �������� ca�ch����� a���a�� �is�a�c�� ��<br />
s���c����� a c����a� i�p��v������� �f �h�� s��pa�a�i�� �f<br />
c��ass��s ca� ��� ��s���v��� �� �h�� �����c��� �����i�i-<br />
����si��a�� spac���� i��ica�i�� �is�i�c� T�ich�p����a<br />
ass������a���s i� �h�� ���i�a�i�� �ia��a�. Th��<br />
relationship between the classification used in<br />
�h�� p���s���� s���y �i.��.�� �yp�����y �f s����a�s� a��<br />
��h��� ����ps �f i�v��������a���s �� ��h��� �i�����ica��<br />
elements (e.g. phytobenthos, macrophytes, fish)<br />
has to be verified in order to allow for sensitive<br />
a�� acc��a��� �i�ass��ss�����s. W�� c��si���� �ha�<br />
robust physical classifications are necessary for<br />
wa���� �a�a�������� p��p�s��s ��sp��cia����y ���ca�s��<br />
�h��y a��� ��asi��y ������s���� a�� c�����ica����.<br />
The relationship between a priori classifications<br />
a�� �i�����ica�� ass������a���s �i�h� ��� i�p��v���<br />
if w�� f�c�s �� �h�s�� �a�a�� which hav�� ���h<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
�a���w ��c�����ica�� ���q�i��������s a�� i��������-<br />
�ia��� a����a�c��s �i.���� ��� �h�� ��� �a��� �� �h�� ���<br />
c����� sp��ci��s�. Th�� p���s���� s���y s�����s�s<br />
�ha� �h�s�� sp��ci��s a��� f��w. H�w��v����� if �h��y a���<br />
s������c���� f�� �i�ass��ss������� a� i�p��v�������<br />
�f �h�� �isc�i�i�a�i�� ����w����� physica�� c��ass��s<br />
a����� wi�h a ���c���as�� �f �h�� h�������������i�y wi�hi�<br />
physica�� c��ass��s �i�h� ��� ���p��c����.<br />
Acknowledgements<br />
This w��� has ������ ca��i��� ��� i� �h�� f�a���w��� �f<br />
several projects: (1) the field work was organized<br />
and financed by Centre de Recherche Public –<br />
Ga��i���� �ipp�a�� a�� ��s��� Na�i��a�� ��His��i��� �His��i��� His��i���<br />
Na����������� i� ����������� i� �h�� f�a���w���<br />
�f �h�� p��j��c�s "Rhi�h���" a�� "P��a���"; �2�<br />
�h�� ���������c���� p��j��c� was f������ �y �h��<br />
����������� Na�i��a�� F��� f�� R��s��a�ch.<br />
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<strong>Ferrantia</strong> • 55 / 2008
A. Gashi, H. Ibrahimi Spatial and temporal distribution of <strong>Trichoptera</strong> larvae in the Mirusha River (Kosova)<br />
Spatial and temporal distribution of <strong>Trichoptera</strong><br />
larvae in the Mirusha River (Kosova)<br />
Abstract<br />
I� �his pap��� �h�� spa�ia�� a�� ����p��a�� �is��i���i�� �f<br />
T�ich�p����a ��a�va�� i� �h�� �i��sha Riv��� �K�s�va� was<br />
s���i���. ������� sa�p����s w����� �a���� a� si� s������c����<br />
s�a�i��s �w� �i���s p��� ����h ���i�� a ����-y��a� p���i��.<br />
Th�� a����a�c�� �f T�ich�p����a ��a�va�� va�i��� ����a���y i�<br />
space and time. Three different families of <strong>Trichoptera</strong><br />
Introduction<br />
<strong>Trichoptera</strong>, or caddisflies, comprise one of the<br />
��s� �iv���s�� aq�a�ic i�s��c� ������s. Th�� ��a�va��<br />
s�a���s a��� f���� i� ��a���s�� �iv���s�� a�� s����a�s a��<br />
a��� i�p���a�� c��p������s �f f��� w���s i� �h��s��<br />
f���shwa���� ��c�sys����s �R��sh a�� R�s��������<br />
1984). Almost 12,000 caddisfly species, belonging<br />
�� 4� fa�i��i��s a�� a���� 600 �������a�� hav�� ������<br />
���sc�i���� f��� a���� fa��a�� ����i��s�� ��� i� has ������<br />
��s�i�a���� �ha� �h�� w����� fa��a �ay c���ai� as<br />
��ch as 4���000 sp��ci��s ��ch�i� 1984�.<br />
T�ich�p����a i�v��s�i�a�i��s i� K�s�va a��� �ai���y<br />
sp��a�ic a�� ��s���y i�c������� wi�hi� �������a��<br />
s���i��s �f �����hic �ac��i�v��������a���s.<br />
Th�� �i��sha Riv��� ca�ch����� is ���ca���� i� �h��<br />
w��s����� pa�� �f K�s�va. Th�� ���a�� �������h �f �h�� �iv���<br />
is a���� 29 ���� si��a���� a����� �h�� �������s �f �h��<br />
B��ac� ���a�� ������a� a�� ���ia�ic ���a ca�ch�����s.<br />
Th�� ai� �f �his s���y was �� ���p������ spa�ia��<br />
and temporal distribution patterns along the<br />
�iv��� a�� �h����h��� �h�� y��a�. Th�� p���c����a���<br />
�f T�ich�p����a ��a�va�� wi�h ���sp��c� �� �h�� �v���a����<br />
�ac��i�v��������a��� fa��a was a��s� ��������i���� a�<br />
s������c���� s�a�i��s.<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Agim Gashi<br />
Halil Ibrahimi<br />
U�iv���si�y �f P�ish�i�a<br />
Fac����y �f Na���a�� �ci���c��s<br />
Prishtina – Kosova<br />
ha��i��i��ahi�i@yah��.c��<br />
w����� f���� �Rhyac�phi��i�a���� Hy���psychi�a�� a��<br />
�i����phi��i�a��� wi�h 10 �a�a i� ���a��. Th�� p���c����a���<br />
�f T�ich�p����a i� �v���a���� �ac�����������h�s i�v��������a���<br />
����si�y a�� �s�a��i�� c��p� �i��ass was ca��c���a���� as<br />
w������.<br />
Material and Methods<br />
Quantitative samples were taken with a Surber<br />
sa�p����� �30 � 20 c��� 600 c� 2 � ���i�� 1989 - 1990.<br />
���i�i��a�� sa�p����s w����� �a���� ���i�� 2001. Th��<br />
criteria for choosing sampling stations were: type<br />
a�� s���p�� �f �h�� �iv��� �a��� a���i����� a�� v������a�i��<br />
s���c�����. Th�� c�������c���� �a����ia�� was p���s���v��� i�<br />
4 % f���a�����hy���. I� �h�� ��a���a���y�� �h�� �a����ia��<br />
was s������ ��� a�� �h�� ��a�va�� �f T�ich�p����a w�����<br />
identified and transferred to 75% ethanol. The<br />
�a����ia�� was ��������i���� a� �h�� D��pa������� �f<br />
Bi�����y �U�iv���si�y �f P�ish�i�a - K�s�va� wi�h<br />
c���i����s assis�a�c�� �y ���p����s f��� I�s�i����� �f<br />
Z������y �f �h�� B����a�ia� �ca����y �f �ci���c��s.<br />
Results<br />
Th�� i�v��s�i�a�i��s a� si� s������c���� s�a�i��s a�����<br />
�h�� �i��sha Riv��� yi�������� 10 �a�a �f T�ich�p����a<br />
��������i�� �� �h����� fa�i��i��s �Ta����� 1�.<br />
�� s�a�i�� �1 s��v��� �a�a �f T�ich�p����a w����� f����.<br />
Th�� ��s� f���q����� �a�a p��� s��fac�� ��i� f�� �his<br />
s�a�i�� is Hydropsyche sp.�� which is p���s���� ��s���y<br />
57
A. Gashi, H. Ibrahimi Spatial and temporal distribution of <strong>Trichoptera</strong> larvae in the Mirusha River (Kosova)<br />
58<br />
Table 1. Distribution of species of <strong>Trichoptera</strong> (larvae) at six selected stations of the Mirusha River.<br />
in summer – autumn. Hydropsyche sp. ���. i�s�a�i��is�<br />
was p���s���� �h����h��� a���� s��as��s ��� i� sh�w���<br />
�h�� ����a���s� ����si�y ���i�� J���y. Rhyacophila nubila,<br />
(Zetterstedt, 1840) and Rhyacophila sp. ���. v����a�is�<br />
a��� p���s���� a� ���w ����si�i��s ���i�� wi�����-sp�i��.<br />
�� s�a�i�� �2 Rhyacophila sp. ���. v����a�is� a��<br />
Rhyacophila nubila a��� p���s���� i� a���� s��as��s<br />
��� i� s�a���� �������s. Hydropsyche sp. ���.<br />
guttata) reaches high abundances during spring.<br />
Hydropsyche sp. ���. p�������ci����a� a�� Limhephilidae<br />
gen. sp. w����� f���� ����y �w� �i���s a� �his s�a�i�� i�<br />
�a�ch a�� �p�i��. Hydropsyche sp. ���. i�s�a�i��is� is<br />
p���s���� i� a���� s��as��s ��� ��s� f���q�������y ���i��<br />
s������. D���s�� p�p���a�i��s �f Hydropysche sp. a���<br />
���ach��� ���i�� �h�� ���� �f �h�� s������ a�� ���i��<br />
�h�� a�����. Stenophylax sp. a�� Potamophylax sp.<br />
w����� f���� ����y ��c�� i� v���y s�a���� �������s p���<br />
s��fac�� ��i�.<br />
O���y �w� �a�a w����� f���� a� s�a�i�� �3 ���i��<br />
summer and autumn: Hydropsyche sp. (gr. guttata)<br />
a�� Hydropsyche sp..<br />
�� s�a�i�� �4 f��� �a�a �f fa�i��y Hy���psychi�a��<br />
a��� p���s����. Hydropsyche sp. ���. i�s�a�i��is� is sca�c��.<br />
Hydropsyche sp. (gr. guttata) is sub-dominantly<br />
p���s���� ���i�� a���� s��as��s. Hydropsyche sp. ���.<br />
p�������ci����a� a�� Hydropsyche sp. a��� p���s���� a����s�<br />
in equal numbers but they differ in their seasonal<br />
Stations<br />
Taxa M1 M2 M3 M4 M5 M6<br />
Rhyacophilidae<br />
Rhyacophila nubila + + +<br />
Rhyacophila sp. ���. vulgaris� + + +<br />
Rhyacophila sp. +<br />
Hydropsychidae<br />
Hydropsyche sp. ���. guttata� + + + + + +<br />
Hydropsyche sp. ���. pellucidula� + + + +<br />
Hydropsyche sp. ���. instabilis� + + + + +<br />
Hydropsyche sp. + + + + +<br />
Limnephilidae<br />
Limnephilidae ����. sp. +<br />
Stenophylax sp. +<br />
Potamophylax sp. + +<br />
distribution. The first one is present during wintersp�i����<br />
�h�� s��c��� ���i�� s������-a�����.<br />
F��� �a�a �f T�ich�p����a w����� f���� a� s�a�i�� ��.<br />
Hydropsyche sp. (gr. guttata) and Hydropsyche sp.<br />
a��� ���h s�����i�a�� wh�����as Hydropsyche sp ���.<br />
guttata) is present continually during the whole<br />
y��a� ���c��p� �a�ch. Hydropsyche sp. ���. p�������ci����a�<br />
is p���s���� ���i�� �h�� ���� �f �h�� wi������� ���i�� �h��<br />
s������ a�� ���i�� sp�i��. Hydropsyche sp. ���.<br />
i�s�a�i��is� a�� Hydropsyche sp. w����� ��� f���� i�<br />
sp�i��.<br />
�i� �a�a w����� f���� a� s�a�i�� �6. Rhyacophila<br />
nubila is p���s���� a� ���w a����a�c��s ���i��<br />
a���� s��as��s ���c��p� wi�����. Rhyacophila sp. ���.<br />
v����a�is� is p���s���� ���i�� �ay a�� Oc�������� a��<br />
Rhyacophila sp ���i�� J������ Oc������ a�� D��c�������.<br />
Hydropsyche sp. (gr. guttata) is the most abundant<br />
T�ich�p����a �a��� a� �his s�a�i��. Hydropsyche sp.<br />
���. i�s�a�i��is� is p���s���� a� ���w ����si�i��s ���i��<br />
sp�i��-s������ wh�����as Hydropsyche sp. is p���s����<br />
���c���siv����y ���i�� a�����.<br />
Th�� ���a� p���c����a��� �f T�ich�p����a wi�h ���sp��c�<br />
�� �v���a���� �ac�����������h�s ����si�y �f �h�� �i��sha<br />
river sampling sites was 14.1 % with specific<br />
s�a�i��s �a��i�� f��� 0.8� % �s�a�i�� �3� �� 42.28<br />
% �s�a�i�� ��� �Fi�.1�.<br />
<strong>Ferrantia</strong> • 55 / 2008
A. Gashi, H. Ibrahimi Spatial and temporal distribution of <strong>Trichoptera</strong> larvae in the Mirusha River (Kosova)<br />
50<br />
40<br />
30<br />
20<br />
10<br />
0<br />
Th�� ���a� p���c����a��� i� �����s �f �s�a��i�� c��p�<br />
�i��ass �f �v���a���� �����hic i�v��������a���s was 16.8<br />
% wi�h s�a�i��s �a��i�� f��� 0.09 % �s�a�i�� �3�<br />
�� �6.3� % �s�a�i�� �4� �Fi�. 2�.<br />
Discussion and Conclusions<br />
I� �h�� p���s���� s���y �h�� c����i���i�� �f T�ich�p����a<br />
wi�hi� �v���a���� �ac�����������h�s was �p �� 14.1<br />
% i� �����s �f ����si�y a�� 16.8 % i� �����s �f<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
16.34<br />
6.73<br />
0.85<br />
33.6<br />
42.28<br />
9.13<br />
M1 M2 M3 M4 M5 M6<br />
Fig. 1: The percentage of <strong>Trichoptera</strong> larvae with respect to overall macrozoobenthos density at six selected<br />
stations of the Mirusha River.<br />
70<br />
60<br />
50<br />
40<br />
30<br />
20<br />
10<br />
0<br />
35.99<br />
16.44<br />
0.09<br />
s<br />
Fig 2: Percentage of <strong>Trichoptera</strong> larvae in terms of 'standing crop' biomass of overall macrozoobenthos at<br />
six selected stations of the Mirusha River<br />
s<br />
56.35<br />
33.99<br />
9.93<br />
M1 M2 M3 M4 M5 M6<br />
�s�a��i�� c��p� �i��ass. This is i� a�����������<br />
wi�h ��h��� si�i��a� s���i��s. F�� ���a�p������ �icha<br />
�1970� ���p������ �ha� i� a B�����ia� �iv��� T�ich�p����a<br />
c��s�i������ a���� 20% �f ���a�� �i��ass �f a����<br />
i�v��������a���s p��� s��fac�� ��i�. Th�� p���c����a��� �f<br />
16.8 % f�� T�ich�p����a i� �i��sha Riv��� w�����<br />
be even higher when Gastropoda were omitted<br />
which w����� ���as����� wi�h sh������.<br />
Among taxa identified genus Hydropsyche made<br />
�p �h�� ��s� i�p���a�� f�ac�i�� �f �ac�����������h�s.<br />
�p��ci��s �f �his �����s w����� p���s���� a���� �v��� �h��<br />
59
A. Gashi, H. Ibrahimi Spatial and temporal distribution of <strong>Trichoptera</strong> larvae in the Mirusha River (Kosova)<br />
60<br />
y��a��� which is i� a����������� wi�h ��h��� si�i��a�<br />
i�v��s�i�a�i��s ��v�y��i�� 1988�� Fi��ip�vic�� 1968�.<br />
Hi�h��s� �a�a �ich���ss was ��s���v��� a� s�a�i�� �2<br />
��i��� �a�a� whi���� a� s�a�i�� �3 ����y �w� �a�a w�����<br />
f����. Th�� s���c����� �f ��h��� �����hic i�v��������a���<br />
����ps a� s�a�i�� �3 was v���y p��� as w������. Th��<br />
���as�� f�� �his a��� ��if��� c��i�a��� c���i�i��s<br />
���i�� �h�� y��a� a�� ��sp��cia����y �����a�iv����y c��s�a��<br />
water temperature (23 – 25 ºC) throughout all the<br />
s��as��s.<br />
References<br />
�v�y��i�� B. 1988. - Rasp�s��a�j���j�� ��ici��i<br />
T�ich�p����a � ������s� i��v��is��� p����cja<br />
Bijelog Drima, Magistarski rad, Prirodoslovno-<br />
�a����a�ic�i fa�������� �v���ci��is�a � Za������.<br />
Fi��ip�vic�� D. 1968. - �i������s�a �a�a�����is�i�a<br />
i��v��s��� ����i��a �isi�s��� p����a �a<br />
Kopaoniku. – Arhiv biol. nauka, Beograd, 19<br />
1-2. - 67-74.<br />
�icha�� J. C. 1970. - E����� q�a��i�a�iv�� �� �����h�s<br />
������ �ivi����� ��� B�����iq����� �������h�� ��i������is��.<br />
– Annales de Limnologie, 6, 3, 255 – 280.<br />
R��sh�� V.H. & R�s���������� D. �. ����i���s� 1993.<br />
- F���shwa���� Bi����i���i�� a�� B����hic<br />
�ac��i�v��������a���s. Chap�a� Chap�a� a�� a�� Ha����. Ha����. N��w N��w<br />
Y���.<br />
�ch�i��� F. 1984. - U� ��ssai ���va���a�i�� ��� ��a fa����<br />
����ia���� ���s T�ich�p���s. Pa��� Pa��� 337 i� i� J.C.<br />
���s�� ���i����. P��c�����i��s �f �h�� 4�h I������a-<br />
�i��a�� �y�p�si�� �� T�ich�p����a. D�. W. J�����<br />
P����ish���s. Th�� Ha����.<br />
<strong>Ferrantia</strong> • 55 / 2008
B. Gullefors Limes norrlandicus - a natural biogeographical border for caddisflies (<strong>Trichoptera</strong>) in Sweden<br />
Limes norrlandicus - a natural biogeographical<br />
border for caddisflies (<strong>Trichoptera</strong>) in Sweden<br />
Abstract<br />
Of �h�� 222 ���w� T�ich�p����a sp��ci��s i� �w������ ��s�<br />
sp��ci��s a��� f���� a���� �v��� �h�� c�����y�� 2� sp��ci��s hav�� a<br />
s���h���� �is��i���i�� whi���� �3 a��� �ai���y i� �h�� ����h.<br />
Th�� ������� "�i���s N�����a��ic�s" is �ai���y �s��� f��<br />
Introduction<br />
H. D. J. Wallengren was the first person who<br />
��i��� �� �iv�� a c��p������� c��pi��a�i�� �f wha� was<br />
known about the caddisflies in Sweden at the<br />
���� �f �h�� 19 �h c������y. H�� ����w 166 sp��ci��s i�<br />
�ca��i�avia�� i.��. �w������ a�� N��way ������h���.<br />
Wa������������ �1884�� 1890�� 1891� a�����a�y ���sc�i����<br />
some of the Swedish caddisflies as living in the<br />
s���h �f �w������ whi���� ��h���s w����� f���� ����y i�<br />
�h�� ����h���� pa��s �f �h�� c�����y.<br />
We didn�t get a checklist of the Swedish caddisflies<br />
���i�� 1942�� wh��� K.-H. F��ss����� a�� B� Tj������<br />
��is���� �h�� 208 sp��ci��s �is��i������ i� �h�� 30 �w���ish<br />
fa��a p��vi�c��s. F��ss����� �19�3� s�pp������������<br />
�h��i� ch��c�-��is� a�� �h�� ������� �f ���w� �w���ish<br />
T�ich�p����a i�c���as��� �� 211 sp��ci��s.<br />
�v���ss�� & Tj������ �197�� ���vis��� �h�� �w���ish<br />
ch��c�-��is� i�c����i�� a���� T�ich�p����a sp��ci��s ���w�<br />
i� NW E���p��. Th�� T�ich�p����a sp��ci��s ���w�<br />
i� �w������ w����� a� �ha� �i��� 216. Th�� ���w�<br />
�w���ish T�ich�p����a sp��ci��s ha� 1988 i�c���as��� ��<br />
219 wh��� �h�� �is��i���i�� i� �h�� ����h���� �w���ish<br />
p��vi�c��s a��s� was p���s������� �G�������f��s 1988�.<br />
Today the number of Swedish caddisfly species is<br />
222 �G�������f��s 2002�.<br />
Th�� ���w�������� �f �h�� �is��i���i�� a���as f�� s����<br />
sp��ci��s is ��� c��p������� ��� �h�� ch��c���is� �f ���ay<br />
shows a clear pattern for most of the 222 species.<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Bo Gullefors<br />
�a�i��p��a� 2<br />
�E- 824 41 H��i�sva������ �w������<br />
��.��������f��s@h��i�sva����.s��<br />
���a�ica�� p��p�s�� ��� ca� a��s� ��� ����a����� as a �a���a��<br />
northern border for caddisflies from southern areas and<br />
a natural southern border for caddisflies living in the<br />
����h���� pa�� �f �w������.<br />
The majority of the Swedish caddisflies (151) can<br />
be found almost all over the country. Twenty five<br />
sp��ci��s hav�� ������ c�������c���� �ai���y i� �h�� s���h����<br />
provinces. Fifty three species have a northern<br />
�is��i���i�� �Ta�s. 1-3��� �f �h�s�� a����� h�w��v�����<br />
13 sp��ci��s wi�����y �is��i������ i� ��h��� pa��s �f<br />
E���p��. Th�� ����h���� �is��i���i�� i� �w������ �f<br />
�h��s�� sp��ci��s ��s� ��� f���h��� i�v��s�i�a����. Th��y<br />
�i�h� ��� �v����������� �� �h�� s���h���� p��vi�c��s<br />
�ay ��� hav�� s�i�a����� ha�i�a�s f�� �h��s�� sp��ci��s.<br />
���v���a�� �f �h�� sp��ci��s ��s� ��� ����a����� as �����i���<br />
����h���� sp��ci��s a�� a��� a��s� ���p������ f��� a f��w<br />
c�����i��s �� �h�� c���i�����.<br />
Limes norrlandicus<br />
The pattern that can be distinguished for the southern<br />
��ivi�� sp��ci��s sh�ws �ha� �h��i� ����h���� p���iph���a��<br />
������ �s�a����y ����s��� c��ss �h�� ������� ca������� �i���s<br />
������a��ic�s �Fi�. 1�. This ������� was ��i�i�a����y<br />
i�v������� �y ���a�is�s i�����ifyi�� �h�� �is��i���i��<br />
�f �w���ish p��a��s. �i���s ������a��ic�s has i�s<br />
c�������pa�� i� �h�� �i���s ��a��a���ic�s i� Ca�a�a.<br />
�i���s ������a��ic�s �ivi���s �h�� ����h���� �����a��<br />
f����s�s a�� a��pi��� a���as f��� �h�� s���h���� pa�� �f<br />
�h�� c�����y �ai���y c��sis�s �f a��ic������a�� ��a��<br />
a�� �i���� f����s�s. �i���s ������a��ic�s is��� a sha�p<br />
������� ��� sh����� ��� ����a����� as a ��a�si�i�� ������.<br />
�i���s N�����a��ic�s s�a��s i� Os��� i� N��way a��<br />
����s �h����h �h�� s���h���� pa�� �f �h�� p��vi�c�� �f<br />
61
B. Gullefors Limes norrlandicus - a natural biogeographical border for caddisflies (<strong>Trichoptera</strong>) in Sweden<br />
62<br />
Fig. 1 Fig. 2 Fig. 3 Fig. 4<br />
Fig. 1: The border Limes norrlandicus in Sweden divides the northern boreal forests and alpine areas from the<br />
southern part of the country mainly consists of agricultural land and mixed forests.<br />
Fig. 2: The Limes norrlandicus acts as a northern border for the distribution area of <strong>Trichoptera</strong> species Ecnomus<br />
tenellus.<br />
Fig. 3: The distribution area of <strong>Trichoptera</strong> species Leptocerus tineiformis.<br />
Fig. 4: The <strong>Trichoptera</strong> species Anabolia concentrica can be regarded as a characteristic species for those living<br />
north of the Limes norrlandicus.<br />
Vä����a���� �h�� p��vi�c��s �f Nä������ Väs��a���a��<br />
a�� s���h���� Da��a��a �� �h�� p��vi�c�� �f Gäs��i���a��<br />
��jö�s 1967�� 1999�.<br />
Wh���h��� �i���s ������a��ic�s a��s� c��ss��s �h�� p��vi�c��<br />
�f H�si����a�� is��� c����a��� ��� �a�y s���h���� sp��ci��s<br />
f������w �h�� �w���ish c�as� i��� �h�� p��vi�c�� �f<br />
H�si����a��. �i���s ������a��ic�s is a��s� a s���h����<br />
������� f�� ����h���� sp��ci��s.<br />
F�� s���� �f �h�� T�ich�p����a sp��ci��s �i���s<br />
������a��ic�s c����a���y ac� as a ������� ����w�����<br />
����h���� a�� s���h���� ��ivi�� sp��ci��s�� i.��. f�� ���a�p����<br />
�h�� s���h���� sp��ci��s Ecnomus tenellus �Fi�. 2� a��<br />
Leptocerus tineiformis �Fi�. 3� a�� �h�� ����h���� sp��ci��s<br />
Anabolia concentrica �Fi�. 4�.<br />
Discussion<br />
�i���s ������a��ic�s is a p������c��� c��i�a������ica��<br />
a�� �i�������aphica�� ������� f�� �a�y p��a��s<br />
f��� �h�� s���h (Quercus robur �Oa���� Fraxinus<br />
excelsior ��sh� a�� Corylus avellana �Ha�������� a��<br />
�i��s (Strix aluco �Taw�y �w��� a�� Picus viridis<br />
�G������ w���p��c�����. Th�� p��a��s Lactuca alpina,<br />
Betula nana a�� Sparganium hyperboreum a�� �h��<br />
�i��s Fringilla montifringilla �B�a���i����� Lanius<br />
excubitor �G���a� ����y sh�i���� a�� Lagopus lagopus<br />
(Willow ����s��� hav�� �i���s ������a��ic�s as a<br />
s���h���� �������. �v���ss�� �1992� has i� his s���y<br />
�f a����� �y�i�i�s �C������p����a� sh�w� �ha� �h��<br />
������� is a��s� va��i� f�� �h�� ����h���� ��ivi�� sp��ci��s<br />
Gyrinus opacus �ah�������. Th�� �is��i���i�� a���as �f<br />
�h�� �w� s���i��� s���h���� sp��ci��s�� G. natator a��<br />
G. substriatus, c��ss �h�� �i���s ������a��ic�s.<br />
The distribution of the listed caddisflies is based<br />
on the findings in Sweden. I believe that some<br />
sp��ci��s c����� ��� �issi�� �� a� ����as� ��� ���c������<br />
i� �h�� s���h �f �w������ ���� �� ac�ivi�i��s i� �h��<br />
��a��scap�� c��c����i�� ��a�� �s���� cha����s �f ai�-<br />
and water conditions, influences by human<br />
ac�ivi�i��s ���c. �� �� �h��y si�p��y ��ac� s�i�a�����<br />
habitats for their development? Some of the<br />
sp��ci��s �ha� Wa������������ �1891� �i���� ���c��� a�<br />
a���� �� ����y ���c������ as �a��� a� s���� s�a���� ���ca��<br />
<strong>Ferrantia</strong> • 55 / 2008
B. Gullefors Limes norrlandicus - a natural biogeographical border for caddisflies (<strong>Trichoptera</strong>) in Sweden<br />
Tables 1-3: Caddisfly species with their main distribution areas in North and South Sweden and data<br />
about their distribution in Europe. Data from Sweden are taken from Gullefors (2002,<br />
2003, 2004, 2005) and data about European distribution are from Wiberg-Larsen (2004).<br />
Table 1: Forty species with a northern distribution in Sweden:<br />
Country designations: �E = �w�������� NO = N��way�� F�� = Fi���a���� EE = Es���ia�� �� = �a�via�� DK = D����a���� UK = U�i���� Ki�������<br />
DE = G����a�y�� P� = P���a���� � = ��s��ia�� BU = B����a�ia�� ��K = ����va�ia�� CZ = C����ch R��p����ic�� RO = R��a�ia�� ��N = ����v���ia�� FR =<br />
F�a�c��<br />
Species Distribution in Europe:<br />
Glossosoma nylanderi �c�ach��a� 1879 �E�� NO�� FI<br />
Oxyethira boreella �v���ss�� & Tj������ 197� �E�� FI<br />
Oxyethira ecornuta ������ 1893 �E�� FI�� ��<br />
Oxyethira klingstedti Ny��� 1983 �E�� FI<br />
Oxyethira mirabilis ������ 1904 �E�� NO�� FI�� ���� UK�� FR<br />
Plectrocnemia conjuncta �a��y��v 1914 �E�� FI�� EE�� P�<br />
Arctopsyche ladogensis �K������a�i 18�9� �E�� NO�� FI�� ��<br />
Agrypnetes crassicornis �c�ach��a� 1878 �E�� FI�� EE�� UK<br />
Agrypnia colorata Ha���� 1873 / Agrypnia<br />
principalis ��a��y��v 1909�<br />
�E�� FI<br />
Agrypnia czerskyi ��a��y��v 1924� �E�� FI<br />
Agrypnia sahibergi ��c�ach��a� 1880� �E�� NO�� FI<br />
Micrasema gelidum �c�ach��a� 1876 �E�� NO�� FI�� EE<br />
Apatania dalecarlica �F��ss����� 1930� �E<br />
Apatania forsslundi T��ias�� 1981 �E<br />
Apatania hispida �F��ss����� 1930� �E�� NO�� FI<br />
Chaetopteryx sahibergi �c�ach��a� 1876 �E�� NO�� FI�� EE�� P��� RO<br />
Brachypsyche sibirica ��a��y��v 1924� �E�� FI<br />
Anabolia concentrica (Zetterstedt 1840) �E�� NO�� FI�� EE�� ���� RO<br />
Anabolia laevis (Zetterstedt 1840) �E�� NO�� FI�� EE�� ���� P��� RO�� FR<br />
Arctopora trimaculata (Zetterstedt 1840) �E�� NO�� FI�� EE<br />
Asynarchus contumax �c�ach��a� 1880 �E�� NO�� FI<br />
Asynarchus impar �c�ach��a� 1880 �E�� NO�� FI<br />
Asynarchus lapponicus (Zetterstedt 1840) �E�� NO�� FI�� ��� BU�� RO<br />
Asynarchus thedenii �Wa������������ 1879� �E�� NO�� FI<br />
Grammotaulius signatipennis �c�ach��a� 1876 �E�� NO�� FI�� EE�� ���� P�<br />
Lenarchus bicornis ��c�ach��a� 1880� �E�� FI�� EE�� P�<br />
Lenarchus productus ������� 1896� �E�� NO�� FI<br />
Limnephilus algosus ��c�ach��a� 1868� �E�� NO�� FI�� DE�� ��� ��K�� CZ<br />
Limnephilus diphyes �c�ach��a� 1880 �E�� NO�� FI�� EE�� ��K�� CZ<br />
Limnephilus dispar �c�ach��a� 187� �E�� NO�� FI�� EE�� ���� DK�� DE�� P�<br />
Limnephilus externus Ha���� 1861 �E�� NO�� FI�� ���� DE�� P�<br />
Limnephilus femoralis Ki��y 1837 �E�� NO�� FI<br />
Limnephilus feinoratus (Zetterstedt 1840) �E�� NO�� FI�� EE<br />
Limnephilus fenestratus (Zetterstedt 1840) �E�� NO�� FI�� EE�� ICE<br />
Limnephilus picturatus �c�ach��a� 187� �E�� NO�� FI�� EE�� ICE<br />
Limnephilus subnitidus �c�ach��a� 187� �E�� NO�� FI<br />
Molanna nigra (Zetterstedt 1840) �E�� FI�� EE�� DE�� CZ<br />
Molanna submarginalis �c�ach��a� 1872 �E�� FI�� EE<br />
Ceraclea excisa ������� 1904� �E�� FI�� P�<br />
Triaenodes unanimis �c�ach��a� 1877 �E�� NO�� FI�� EE�� ���� DE<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
63
B. Gullefors Limes norrlandicus - a natural biogeographical border for caddisflies (<strong>Trichoptera</strong>) in Sweden<br />
64<br />
Table 2: Thirteen species which are mainly found in the northern part of Sweden but are widely distributed<br />
in Europe:<br />
Species Found in No of European countries<br />
Rhyacophila obliterata �c�ach��a� 1863 19<br />
Glossosoma intermedium K��apa����� 1892 13<br />
Hydroptila lotensis ��s����y 1930 1�<br />
Hydroptila occulta �Ea��� 1873� 19<br />
Hydroptila simulans ��s����y 1920 22<br />
Hydroptila vectis C���is 1834 21<br />
Oxyethira distinctella �c�ach��a� 1880 9<br />
Oxyethira falcata ������ 1893 18<br />
Oxyethira frici K��apa����� 1891 12<br />
Oxyethira simplex Ris 1897 11<br />
Stactobiella risi �F�������� 1908� 11<br />
Micrasema setiferum �Pic���� 1834� 17<br />
Apatania muliebris �c�ach��a� 196� 14<br />
Table 3: Twenty five species with a southern distribution in Sweden:<br />
Species Found in No of European countries<br />
Agapetus fuscipes C���is 1834 17<br />
Ithytrichia clavata ������ 190� 7<br />
Orthotrichia angustella ��c�ach��a� 186�� 19<br />
Orthotrichia costalis �C���is 1834� 20<br />
Orthotrichia tragetti ��s����y1930 14<br />
Tricholeiochiton fagesii �G�i�a�� 1879� 19<br />
Wormaldia occipitalis Pic���� 1834 23<br />
Lype reducta �Ha���� 1868� 24<br />
Tinodes pallidulus �c�ach��a�1878 19<br />
Ecnomus tenellus �Ra���� 1842� 24<br />
Cyrnus crenaticornis �K������a�i 18�9� 19<br />
Anabolia furcata B�a���� 18�7 12<br />
Grammotaulius nitidus �O.F. �ü������� 1764� 18<br />
Limnephilus hirsutus �Pic���� 1834� 22<br />
Limnephilus luridus C���is 1834 11<br />
Limnephilus tauricus �ch�i� 1964 7<br />
Potamophylax rotundipennis �B�a���� 18�7� 18<br />
Beraea maura �C���is 1834� 23<br />
Ernodes articularis �Pic���� 1834� 20<br />
Notidobia ciliaris ��i��a���s 1761� 20<br />
Odontocerum albicorne ��c�p���i 1769� 20<br />
Leptocerus tineiformis C���is 1834 23<br />
Setodes argentipunctellus �c�ach��a� 1877 11<br />
Setodes punctatus �Fa��ici�s 1793� 19<br />
Ylodes reuteri ��c�ach��a� 1880� 11<br />
<strong>Ferrantia</strong> • 55 / 2008
B. Gullefors Limes norrlandicus - a natural biogeographical border for caddisflies (<strong>Trichoptera</strong>) in Sweden<br />
p��ac��s�� ��.�. Ecnomus tenellus, a��� �0 y��a�s ��a����<br />
���sc�i���� wi�h a wi��� �is��i���i�� � F��ss����� &<br />
Tj������ 1942�. N�� Wa������������ �1884�� 1890�� 1891� ��<br />
F��ss����� & Tj������ �1942� �i� �����i�� Leptocerus<br />
tineiformis. Forsslund (1953) was the first to report<br />
���p��c����s �i���if���is f��� �w������ �f��� �h��<br />
�w� p��vi�c��s �ö�����a���a�� a�� Upp��a���.<br />
Fifty years later it is recorded from 21 different<br />
p��ac��s i� ��i�h� p��vi�c��s �G�������f��s 2002�� 2003��<br />
2004�� 200�� a�� was c�������c���� i� a� ��������s<br />
q�a��i�y a� �h�� ��a��� K�a����sjö� i� �h�� p��vi�c�� �f<br />
���� i� 2003 a�� 2004 �G�������f��s ��p����ish����.<br />
Why w����� �h�s�� �w� ���a�p����s f���� s� ��a��� a��<br />
in scattered places? Have the species dispersed or<br />
are earlier only badly investigated?<br />
My classification in southern and northern species<br />
has to be considered as a first attempt to describe<br />
the pattern of the spreading of the caddisflies in<br />
Sweden and will undoubtedly be modified with<br />
i�c���asi�� ���w��������.<br />
Th�� �����a����� �is��i���i�� a���a f�� s���� sp��ci��s<br />
ca� ���p���� �� sp���a�i���� ���� �� c��i�a�ica��<br />
cha����s�� a� ����as� ��wa��s �h�� ����h. B��h Ecnomus<br />
tenellus a�� Leptocerus tineiformis a��� sp��ci��s<br />
p������ssi�� ����hwa��s. N���h���� sp��ci��s<br />
�a�����y sp���a� ��wa��s �h�� s���h. Th�� ����h����<br />
�����a�y �f a sp��ci��s ���p����s �� �h�� c��i�a�����<br />
whi���� �h�� s���h���� �����a�y ���p����s ����� ��<br />
�h�� c��p���i�i�� �f �h�� sp��ci��s ��������s�a� &<br />
�v���ss�� 1996�.<br />
Literature<br />
�������s�a� P. & �v���ss�� B. W. 1996. - �i���s<br />
norrlandicus - där taigan börjar. In: Växter och<br />
djur pp: 36 - 38. Gustafsson L. & Ahlén I. (eds).<br />
�v���i���s Na�i��a��a���as. �N� Fö���a�.<br />
F��ss����� K.-H. & Tj������ B. 1942. - Ca�a�����s<br />
I�s��c����� ����cia��. II. T�ich�p����a. Op�sc���a<br />
Entomologica 7: 92-106.<br />
F��ss����� K.-H. 19�3. - Ca�a�����s I�s��c�����<br />
����cia��. ���i�a�����a a� pa�� II. T�ich�p����a.<br />
Opuscula Entomologica 18: 72-74.<br />
Gullefors B. 1988. - Förteckning över Sveriges natts-<br />
��ä���� �T�ich�p����a��� ���� fy��a��iv����s��� fö� ���<br />
nordliga landskapen. Entomologisk tidskrift<br />
109: 71-80.<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Gullefors B. 2002. - Sveriges nattsländor (<strong>Trichoptera</strong>),<br />
en provinskatalog med nyare fynduppgifter.<br />
Entomologisk tidskrift 123: 131-147.<br />
G�������f��s B. 2003. - Nya �v���s�a p��vi�sfy��<br />
av nattsländor (<strong>Trichoptera</strong>). Entomologisk<br />
tidskrift 124: 193-199.<br />
Gullefors B. 2004. - Nya provinsfynd av natts-<br />
����� �T�ich�p����a� i �v���i��� 2003. E�����logisk<br />
tidskrift 125: 71-73.<br />
Gullefors B. 2005. - Nya provinsfynd av natts-<br />
����� �T�ich�p����a� i �v���i��� 2004. - E�����-<br />
logisk Tidschrift 126: 117-120<br />
Sjörs H. 1967. - Nordisk växtgeografi. Scandi-<br />
�avia� U�iv���si�y B���s 240 pp.<br />
Sjörs H. 1999. - The background: geology, climate<br />
and zonation. In: Eds. Rydin H., Snoeijs P. &<br />
Di����a�� �. �w���ish P��a�� G�����aphy. �c�a<br />
Phy��������aphica. ����cica 84�� �-14.<br />
�v���ss�� B. W. 1992. - Cha����s i� �cc�pa�cy�� �ich��<br />
����a��h a�� a����a�c�� �f �h����� Gy�i��s sp��ci��s<br />
as �h��i� ���sp��c�iv�� �a���� ��i�i�s a��� app��ach���. -<br />
Oikos 63: 147 - 156.<br />
�v���ss�� B.W. & Tj������ B. 197�. - Ch��c�-�is� �f �h��<br />
T�ich�p����a �f N���h-W��s����� E���p��. - E�����logica<br />
Scandinavica 6: 261-274.<br />
Wa������������ H. D. J. 1884. - Fö����c��i�� å. ���<br />
�i���phi��i�a���� �pa�a�i�a�� �ch ����ic�s���atidae<br />
som hittills blifvit funna på Skandinaviska<br />
halfön. - Entomologisk tidskrift 5: 115 -138.<br />
Wa������������ H. D. J. 1890. - Fö����c��i�� öv���<br />
<strong>Trichoptera</strong> Aequipalpina, som hittills blifvit<br />
f���a på ��a��i�avis�a ha��fö�. - E���������is�<br />
tidskrift 11: 1 - 17.<br />
Wa������������ H.D.J. 1891. - ��a��i�avi���s<br />
N�����p����a. II.- K. �v���s�a V������s�. ��a�.<br />
Handl. Bd. 24 No 10: 1 -173.<br />
Wi�����-�a�s��� P. 2004. - Da�ish T�ich�p����a -<br />
sp��ci��s �iv���si�y�� �i�����ica�� ��ai�s�� a�� a�����<br />
�isp���sa��. - Ph.D.- �h��sis 2004. F���shwa���� Bi����-<br />
�ica�� ��a���a���y�� Fac����y �f �ci���c��. U�iv���si�y<br />
�f C�p���ha���� & Fy� c����y�� D��p�. �a����� &<br />
�q�a�ic E�vi��������.<br />
65
B. Higler Distribution of caddisflies in The Netherlands<br />
66<br />
Distribution of caddisflies in The Netherlands<br />
Abstract<br />
1. Th����� is �� ���s�w���hy �v���vi��w �f �h�� �is��i���i��<br />
of caddisflies in The Netherlands.<br />
2. Th�� p���s���� ���w�������� �f �v��� �0.000 ��s���va�i��s<br />
is �ai���y �as��� �� ��a�va���� �a�y �f which hav�� p���a���y<br />
not been identified properly.<br />
3. O��� ���c���s ����f���� �h�� ���c��� W����� Wa�� �f a�����s<br />
suffer from lack of modern literature and are mainly<br />
�as��� �� ��s���va�i��s ���a� h���� a�� f��� ���c��si��s ��<br />
�����������ica�� h�� sp��s.<br />
Introduction<br />
I� p���pa�i�� a �is��i���i�� a���as �f D��ch<br />
T�ich�p����a�� I a� c�������c�i�� �a�a f��� ��i����a����� a��<br />
���p���s�� i�c����i�� a �a�a�as�� �f sp��ci��s c�������c����<br />
�y Wa���� ���h��i�i��s. ������v����� s��v���a�� ��s����<br />
c�������c�i��s hav�� ������ sc���i�i����� �B���sa���a��<br />
200���� Ti������ Na���a�� His���y<br />
��s���� �Hi������ ��� a��. 200�� a�� ���� �a����ia�� f���<br />
���s��a�ch f�� �h�� i�s�i����� wh����� I �s��� �� w���<br />
(at present Alterra) has been re-identified. Some<br />
�0.000 �a�a hav�� ������ c�������c���� a�� p��visi��a����y<br />
�app��� �y E���p��a� I�v��������a��� ���v��y�� wh�����<br />
�h�� ���a�� �a�a�as�� is �ai��ai����.<br />
Results<br />
Th�� �aps a��� a ����a� h����p f�� �h�� i�����p����a�i��<br />
of distribution patterns, which are related to<br />
a�i��ic pa�a�������s s�ch as c������� v�����ci�y�� pH��<br />
������aphica�� va�ia�i�� a�� his���y �f his���ica��<br />
��v����s. I� a��s� ���a�����s �� ��ac�� p���a����� ������s i�<br />
identification.<br />
Bert Higler<br />
H���s��aa� 4<br />
N�-39�6 N� ������s��<br />
�����hi������@h�������.���<br />
4. R��c���� ��s���va�i��s �f a�����s sh�w a� i�c���as�� �f<br />
several species, indicating either the effects of climate<br />
cha���� �� a cha���� i� ha�i�a� �s�� �y �h�� ��a�va�� (Oecetis<br />
notata, Ceraclea dissimilis).<br />
�. R��� ��is�s hav�� �� c��si���� �h�� ���a�� ������aphica��<br />
�a���� �f sp��ci��s i�s���a� �f �a�i��a�� �����a�i��s. "Ra���"<br />
sp��ci��s f��� �h�� s���h������s� pa�� �f Th�� N���h�����a��s<br />
are very common in Central Europe: common species<br />
f��� D��ch s�a��i�� wa����s a��� �a��� i� s�������i��<br />
c�����i��s.<br />
Th�� N���h�����a��s�� a���h���h a s�a���� c�����y<br />
wi�h��� �����ai�s�� ha�����s a ����a� va�i���y �f<br />
standing and running waters, the latter including<br />
�h�� ���w��� ���ach��s �f �h�� �iv���s ����s�� a�� Rhi���.<br />
The division of Holocene and Plistocene is reflected<br />
�y �h�� p���s���c�� �f �i�ch��s�� ��a���s a�� �a�sh��s ��<br />
c��ay a�� p��a� s�i��s i� �h�� H����c����� a�� s���c��s��<br />
s����a�s a�� ���i�����phic ������a�� p����s ��<br />
sa��y s�i��s i� �h�� P��is��c����� pa�� �f �h�� c�����y.<br />
I� �������a���� �h�� ���i�����phic ������a�� p����s hav��<br />
a ���w pH which is ���ha�c��� �y aci� �ai�. Th��<br />
following distribution patterns can be discerned.<br />
1. �p��ci��s �ha� �cc�� a���� �v��� �h�� c�����y ���<br />
often with the exception of the Wadden Isles<br />
a�� �h�� is��a��s �f �h�� P��vi�c�� �f Z������a��. Th��<br />
Wa����� Is����s hav�� a ���w��� �iv���si�y �f wa����<br />
�yp��s a�� p���a���y �h��y a��� ��� ��asy �� ���ach<br />
wi�h �h�� p���vai��i�� w��s����� wi��s. Th�� is��a��s<br />
of the province of Zeeland have been flooded<br />
�y �h�� s��a i� 19�3 a�� v���y f��w sp��ci��s hav��<br />
reached this area afterwards. (Fig. 1)<br />
2. �p��ci��s �ha� a��� ���s��ic���� �� �h�� P��is��c����� pa��<br />
�f �h�� c�����y. Th��y ��iv�� i� s���c��s�� ���w��a��<br />
s����a�s �� ���i�����phic ������a�� p����s. �Fi�. 2�<br />
<strong>Ferrantia</strong> • 55 / 2008
B. Higler Distribution of caddisflies in The Netherlands<br />
Fig. 1: Distribution of Triaenodes bicolor in The<br />
Netherlands<br />
Hydropsyche angustipennis (Curtis, 1834)<br />
Fig. 2: Distribution of Hydropsyche angustipennis in<br />
The Netherlands<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Fig. 3: Distribution of Cyrnus insolutus in The Netherlands<br />
Fig. 4: Distribution of Ernodes articulons in The<br />
Netherlands<br />
67
B. Higler Distribution of caddisflies in The Netherlands<br />
68<br />
Hydropsyche conéubernalis Maclachlan, 1865<br />
Fig. 5: Distribution of Hydropsyche contubernalis in<br />
The Netherlands<br />
3. Th����� a��� �� sp��ci��s ���s��ic���� �� �h�� H����c�������<br />
��� s���� hav�� hi�h��s� c��c�����a�i��s i� �h��<br />
p��a�y �a�sh a���as �� �h�� ��a�si�i�� f���<br />
P��is��c����� �� H����c�����. �Fi�. 3�<br />
4. �p��ci��s �ha� a��� ���s��ic���� �� �h�� ��s� s���h����<br />
pa�� �f Th�� N���h�����a��s. Th��s�� a��� sp��ci��s �ha�<br />
������ s�a������ fas� ����i�� s����a�s�� p���a���y<br />
��i���-�ich. �Fi�. 4�<br />
5. Species with a distribution pattern along the<br />
��a���� �iv���s. Th��s�� a��� sp��ci��s ��ivi�� i� �h��<br />
�iv���s a�� �s�����i���s� ��i���a�i��s. �Fi�. ��<br />
Problems with the data<br />
Th����� a��� s��v���a�� �yp��s �f p��������s wi�h �h�� �a�a.<br />
• Old records, based on adult identifications,<br />
sometimes suffer from more recent taxonomical<br />
cha����s. Esp��cia����y i� �h�� �����s Hy���psych����<br />
Hy���psych����<br />
�his �ay ����a� �� a w���� pic�����. Hydropsyche<br />
guttata a�� H. ornatula hav�� ������ ���c������<br />
f��� Th�� N���h�����a��s �Fisch��� 1934��� ��� �h��y<br />
c����ai���y �� ��� �cc�� h�����.<br />
• Th�� �����������is�s i� �h�� ����i��i�� ha��f �f �h��<br />
�w����i���h c������y c�������c���� ���a� �h��i� h����s<br />
�� �h��y ��av������� �y ��ai� �i� s�i�s wi�h ha�� ��<br />
y��a���y ���a�i����� ������i��s i� w������ ���w� h��<br />
sp��s �f ���a��if��� �a����� �� �����������ica��<br />
�ich���ss. Th����� w����� �� hi�hways a�� ���<br />
�a�y ca�s. Th�� �aj��i�y �f wa����s w����� ha����y<br />
�� ��� acc��ssi����� a�� �h�� s�-ca������� ���i�a�y<br />
wa���� �yp��s as �i�ch��s �� p���s w����� ��vi��s��y<br />
not interesting because of their superfluous<br />
p���s���c��. Th��i� i���as a���� a����a�c��<br />
a�� �a������ss �f sp��ci��s a��� �as��� �� �h��s��<br />
���p���i���c��s.<br />
• Identifications of larvae are very unreliable,<br />
���ca�s�� �h�� ��i����a����� was sca�c���� i�c��p�������<br />
a�� s�����i���s i�c�����c�. O���y si�c�� �h��<br />
���v����i��s�� ���s�w���hy ���ys hav�� ������<br />
p����c���.<br />
• D��spi��� �h�� p���s���c�� �f v���y ���� f����i��<br />
���ys, larval identifications are often<br />
q���s�i��a�����. Th�� �aj�� pa�� �f �h�� ���c���� �a�a<br />
is f��� ��a�va�� a�� �y c���������i�� "s��a����"<br />
data, identifications proved always to be<br />
fa��s��. O��� ca� hav�� q���s�i��s a���� �h�� �����<br />
c����� sp��ci��s.<br />
• ��s� ���c���� �a�a a��� from Wa���� ���h��i�i��s<br />
(they only collect larvae) with fixed sampling<br />
s�a�i��s. Th�����f����; sp��ci��s a��� �iss����� �ha�<br />
�cc�� i� p��ac��s ���si��� �h��s�� sp��s. �� ca�������<br />
�a��� sp��ci��s hav�� ��� ������ f������ a���h���h<br />
�h��y �ay �cc�� i� �a�y si���s. E�a�p����s a��� w���<br />
�������s��ia�� ha�i�a�s�� s���c��s a�� p��ac��s away<br />
from ��i����s a�� f��� ��h��� p��ac��s�� wh����� ca�s<br />
ca���� pa��.<br />
• Recently, adult caddisflies have been collected<br />
a�� �h��y sh�w a���h��� pic����� �ha� �ha�<br />
p���s������� �y �h�� ��a�va�� �is��i���i��. ����h���h<br />
��� a���� sp��ci��s ca� ��� cap������ �y ��i�h��� i� is<br />
a ����a� h����p �� ��va���a��� �h�� p���s���c�� i� Th��<br />
N���h�����a��s ��wa�ays. Th����� a��� s��v���a��<br />
sp��ci��s �ha� s����� �� i�c���as�� (Oecetis notata,<br />
Ceraclea dissimilis) a�� if s��� �h�� q���s�i�� is why.<br />
� p�ssi�i��i�y is c��i�a��� cha������ ��� i� s�����i���s<br />
�����s ��i��� a cha���� i� ha�i�a� p���f������c��.<br />
It is my firm impression that there is not a<br />
���s�w���hy �v���vi��w �f �h�� �is��i���i�� �f �h��<br />
D��ch T�ich�p����a. Th�� ��s� c����� sp��ci��s a���<br />
p���a���y ���p���s������� w�������� ��� �h����� a��� �a�y<br />
q���s�i��s a���� a �aj��i�y �f sp��ci��s�� which<br />
���s����s i� s��a���� c��s��q����c��s. I� �����s ��i��� �ha�<br />
i���as a���� p���s���c�� a�� a����a�c�� a��� cha��i��<br />
���i�� y��a�s a�� �ha� �h�� ���w�������� �f a����c�����y<br />
is insu���cient.<br />
<strong>Ferrantia</strong> • 55 / 2008
B. Higler Distribution of caddisflies in The Netherlands<br />
C��s��q����c��s f�� �a�i��a�� a�� i������a�i��a��<br />
�����is��a�i��<br />
Th�� D��ch R��� �is� is �ai���y �as��� �p�� �h�� �a�a<br />
f��� Wa���� ���h��i�i��s. Th����� a��� �h����� c�i����ia f��<br />
admittance in the Red List.<br />
• Th�� sp��ci��s is �a��� i� Th�� N���h�����a��s.<br />
• Th�� sp��ci��s is ���c���asi�� i� �������s ��<br />
�cc�pi��� ���ca��i�i��s<br />
• Th�� sp��ci��s has a� i������a�i��a�� i�p���a�c�� f��<br />
�ai�����a�c�� �f i�s p�p���a�i��.<br />
Two out of three of these criteria are su���cient<br />
for admittance to the Red List. It resulted in a list<br />
wi�h 84 �!� sp��ci��s which is ����� �ha� ha��f �f �h��<br />
p���s���� D��ch sp��ci��s. Wha� is �h�� p�ac�ica�� �s�� �f<br />
s�ch a ��is� wi�h sp��ci��s �ha� hav�� ������ ���c������<br />
��c�� �� �0 �� 100 y��a�s a�� f�� �h�� ��as� �i����� s����<br />
of that perhaps wrongly identified? Bureaucratic<br />
���s���s��!<br />
�a�y �f �h��s�� sp��ci��s hav�� ������ i�c������� i� �h��<br />
���f������c�� si��a�i��s �ha� a��� ���i�� �s��� f�� �h��<br />
s�a��a��s �f �h�� E���p��a� Wa���� F�a���w���<br />
Di���c�iv��. This has v���y s��a���� i�p��ica�i��s f��<br />
wa���� �a�a����s�� wh� hav�� �� c��p��y wi�h �h��<br />
E���p��a� ������s i� 201�.<br />
I� �a�y cas��s i� is i�p�ssi����� �� i�p��v��<br />
c���i�i��s i� s�ch a way�� which �����i����� sp��ci��s<br />
a��� �������i��.<br />
I� is ��wis�� �� ���s��ic� ����s����f �� �h�� �a�i��a��<br />
�������s. Th�� �a��� sp��ci��s i� �h�� s���h���� pa��<br />
of the country are often very common in central<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
E���p�� a�� �h�� v���y c����� D��ch sp��ci��s �f<br />
standing waters are often very rare in adjoining<br />
c�����i��s. Wha� is ��������� is a� i������a�i��a���� a<br />
E���p��a��� R��� �is�. Th�� �yp�� �f �is��i���i��-�aps<br />
as p��p�s��� �y Th��as Pi�sch �Pi�sch�� 1981� c�����<br />
��� �s��� a�� i� ��s� ��� ��asy �� �a��� a E���p��a�<br />
R��� �is� �y s���� �f �s wi�h a ���� �v���vi��w �f �h��<br />
si��a�i�� i� E���p��. Of c���s���� �h����� is �h�� i���������<br />
si��� http://www.faunaeur.or� �� ��� �h�� i�f���a�i��<br />
is ��� c��p������� a�� ����y ���a��s wi�h �h�� p���s���c��<br />
�� a�s���c�� i� c�����i��s as p���i�ica�� ��i�s.<br />
Conclusion<br />
K��w�������� �� �h�� �is��i���i�� �f T�ich�p����a is<br />
necessary and useful for scientific, practical and<br />
p���i�ica�� p��p�s��s. Pi�fa����s as i��ica���� ���f���� a���<br />
�a�������s a�� ha��f��� f�� �h�� app��ica�i��i�y i�<br />
wa���� �a�a�������� a�� E���p��a� p���i�ics.<br />
References<br />
B���sa���a�� �. 200�. - I�������s�i�� T�ich�p����a f���<br />
Th�� N���h�����a��s i� �h�� c�������c�i�� �f �h�� Z�����-<br />
�ica�� ��s���� ��s�����a�. E���������isch��<br />
E���������isch��<br />
Berichten 65: 17-20.<br />
Fisch��� F.C.J. 1934. - V�������ich�is ���� i� ����<br />
Ni��������a����� ��� ���� Nach�a�����i�����<br />
vorkommenden <strong>Trichoptera</strong>. Tijdschrift voor<br />
Entomologie 77: 177-201.<br />
69
H. Ibrahimi, A. Gashi State of knowledge of investigations on <strong>Trichoptera</strong> larvae in Kosova<br />
70<br />
State of knowledge of investigations on<br />
<strong>Trichoptera</strong> larvae in Kosova<br />
Abstract<br />
Th�� fa��a �f T�ich�p���a�a i� K�s�va is p�����y s���i���<br />
a�� �h�� i�v��s�i�a�i��s a��� ���i�h��� ����ai����� ��� c��p�������.<br />
Th����� a��� �� �a�a a���� a����� T�ich�p����a a�� �h�� ����ai��s<br />
a���� ��a�va�� �f T�ich�p����a a��� y��� �� ��� ���ai���� f���<br />
�h�� ����a���s� pa�� �f �h�� c�����y. This pap��� p���s����s a<br />
s���a�y �f s���� �f �h�� f������ s���i��s a�� ���c���s<br />
f��� K�s�v�.<br />
Introduction<br />
There are four river Basins in Kosova flowing into<br />
3 �is�i�c� ca�ch�����s �B��ac��� ������a� a�� ���ia�ic<br />
���a� a�� a���h���h �h�� ���� �f s����a�s a�� �iv���s<br />
is v���y w������ ���v�����p��� �h��y a��� p�����y i�v��s-<br />
�i�a����. Esp��cia����y �h�� fa��a �f T�ich�p���a�a is<br />
p�����y s���i��� a�� ��s� �f �h�� i�v��s�i�a�i��s a���<br />
ca��i��� �v��� wi�hi� �h�� �������a�� s���i��s �f �ac��-<br />
���������h�s fa��a�� ���i�� c��c�����a���� �s�a����y ��<br />
��a�va��. I�v��s�i�a�i��s �� �ac�����������h�s fa��a<br />
a��� ��� s� ���� i� K�s�va a�� s���� a��h��s wh�<br />
�����i�� K�s�va’s �iv���s a�� wa����c���s��s i� �h��i�<br />
studies have also analyzed specific aspects of some<br />
a�i�a�� ����ps ��a�����y�� �is��i���i�� �f s����<br />
sp��ci��s�� ��c�����y �f s�a������� ����ps�� �ha� iss���s<br />
�����a���� �� sap���i�����y a�� �i�������aphy�.<br />
Radovanovic (1931) is among the first ones who<br />
i�v��s�i�a���� ��a�va�� �f T�ich�p����a i� Bis��ica<br />
�� P�i������i� Riv���. �� fa� ����ai����� s���i��s ��<br />
�a�����y a�� �is��i���i�� �f ��a�va�� �f T�ich�p����a<br />
w����� ����� i� D�i�i i Ba��hë Riv��� a�� Bis��ica ��<br />
P�i������i� Riv���. ���ss ����ai����� s���i��s �f �ac��-<br />
���������h�s fa��a i�c����i�� ��a�va�� �f T�ich�p����a<br />
w����� a��s� ����� i� �i��sha Riv��� a�� ���api Riv���.<br />
Th�� fa��is�ic �a����ia�� �f s���� �f �h��s�� s���i��s is<br />
deposited in Department of Biology – Faculty of<br />
Na���a�� �ci���c��s i� P�ish�i�a.<br />
Halil Ibrahimi<br />
Agim Gashi<br />
U�iv���si�y �f P�ish�i�a<br />
Fac����y �f Na���a�� �ci���c��s<br />
Prishtina – Kosova<br />
ha��ii��ahi�i@yah��.c��<br />
�cc���i�� �� �h�� p���s���� �a�a i� D�i�i i Ba��hë Riv���<br />
37 �a�a �f T�ich�p����a ��a�va�� a��� ���c�������� i� Bis��ica ��<br />
P�i������i� Riv��� 19 �a�a a��� ���c�������� i� �i��sha Riv��� 10<br />
�a�a a��� ���c������.<br />
O���i�� i�v��s�i�a�i��s �� �ac�����������h�s fa��a<br />
i�c����i�� ��a�va�� �f T�ich�p����a a��� ca��i��� �v��� i� s��v���a��<br />
��h��� s����a�s i� K�s�va<br />
B�����w is a f�a������a�� ��is� �f T�ich�p����a ��a�va��<br />
sp��ci��s f���� i� K�s�va’s �iv���s a�� �h�� �a�a<br />
a��� ��s���y �a���� f��� ��c a�� PhD �h��sis �f<br />
���sp��c�iv�� a��h��s wh� i�v��s�i�a���� �h���.<br />
Results<br />
<strong>Trichoptera</strong> of Bistrica e Prizrenit<br />
River<br />
Confluence of Bistrica e Prizrenit River is mainly<br />
���ca���� i� ����h-w��s� ���w��a��s �f �ha�� �����ai�s.<br />
The approximate surface of this confluence is<br />
a���� 262.� �� 2 . Radovanovic (1931) is the first<br />
���� wh� has c����i������ i�v��s�i�a�i��s �f ��a�va��<br />
�f T�ich�p����a �f �his �iv���. Th�����h i�v��s�i�a-<br />
�i��s �� ��a�va�� �f T�ich�p����a i� Bis��ica Riv���<br />
w����� ����� ��a���� �y � �h���i� �1979�. H����� a��� �h��<br />
results of these findings:<br />
Limnephilidae<br />
Chaetopterygopsis sp.<br />
Drusus sp.<br />
Glyphotaelius pellucidus R�����i�s�� 1783<br />
Stenophylax permistus �c�ach��a��� 189�<br />
<strong>Ferrantia</strong> • 55 / 2008
H. Ibrahimi, A. Gashi State of knowledge of investigations on <strong>Trichoptera</strong> larvae in Kosova<br />
Goeridae<br />
Goera pilosa Fa��ici�s�� 177�<br />
Hydropsychidae<br />
Hydropsyche pellucidula C���is�� 1834<br />
Hydropsyche sp.<br />
Cheumatopsyche lepida Pic������ 1834<br />
Brachycentridae<br />
Micrasema minimum �c �ach��a��� 1876<br />
Oligoplectrum maculatum F���c��y�� 178�<br />
Philopotamidae<br />
Philopotamus montanus�� D���va��� 1813<br />
Rhyacophilidae<br />
Rhyacophila armeniaca G����i�-������vi�������� 1843<br />
Rhyacophila loxias �ch�i��� 1970<br />
Rhyacophila laevis Pic������ 1834<br />
Rhyacophila obliterata �c�ach��a��� 1863<br />
Rhyacophila tristis Pic������ 1834<br />
Rhyacophila sp. (����p vulgaris�<br />
Sericostomatidae<br />
Sericostoma personatum Ki��y & �p���c���� 1826<br />
Sericostoma sp.<br />
<strong>Trichoptera</strong> of Drini i Bardhë River<br />
Th�� s���c�� �f D�i�i i Ba��hë Riv��� is ���ca���� i�<br />
����h���� pa�� �f P��ja ��w� i� a���i����� �f �67�.<br />
Throughout all of its flow until Vërbnica village<br />
wh��� i� pass��s i� �h�� R��p����ic �f ����a�ia�� D�i�i<br />
i Bardhë mainly has got characteristics of field<br />
�iv���. D���ai����� s���i��s �� T�ich�p����a ��a�va�� w�����<br />
����� �y �v�y��i �1988�. 12 fa�i��i��s wi�h 37 sp��ci��s<br />
i� ���a�� w����� f���� ���i�� �h��s�� i�v��s�i�a�i��s.<br />
���i�i��a�� s���i��s w����� a��s� ����� �y G�apci-<br />
K����i �2002�.<br />
Rhyacophilidae<br />
Rhyacophila obliterata �c�ach��a��� 1863<br />
Rhyacophila dorsalis C���is�� 1834<br />
Rhyacophila tristis Pic������ 1834<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Glossosomatidae<br />
Glossosoma discophorum K��apa������� 1902<br />
Agapetus laniger Pic������ 1834<br />
Philopotamidae<br />
Wormaldia subnigra �c�ach��a��� 186�<br />
Polycentropodidae<br />
Plectrocnemia conspersa C���is�� 1834<br />
Polycentropus flavomaculatus Pic������ 1834<br />
Neureclipsis bimaculata �i������ 17�8<br />
Hydropsychidae<br />
Hydropsyche angustipennis C���is�� 1834<br />
Hydropsyche pellucidula C���is�� 1834<br />
Hydropsyche sp.<br />
Cheumatopsyche lepida Pic������ 1834<br />
Limnephilidae<br />
Grammotaulius sp.<br />
Limnephilus rhombicus �i������ 17�8<br />
Limnephilus lunatus C���is�� 1834<br />
Limnephilus sp.<br />
Anabolia laevis Zetterstedt, 1840<br />
Potamophylax latipennis C���is�� 1834<br />
Potamophylax nigricornis Pic������ 1834.<br />
Halesus digitatus �ch�a���� 1781<br />
Halesus radiatus C���is�� 1834<br />
Micropterna lateralis ����ph���s�� 1837<br />
Chaetopteryx villosa Fa��ici�s�� 1798<br />
Annitella obscurata �c �ach��a��� 1876<br />
Drusus discolor Ra������ 1834<br />
Drusus trifidus �c�ach��a��� 1868<br />
Goeridae<br />
Goera pilosa Fa��ici�s�� 177�<br />
Silo pallipes Fa��ici�s�� 1781<br />
Lepidostomatidae<br />
Lepidostoma hirtum Fa��ici�s�� 177�<br />
Brachycentridae<br />
Brachycentrus montanus K��apa������� 1891<br />
Brachycentrus subnubilus C���is�� 1834<br />
Odontoceridae<br />
Odontocerum albicorne �c�p���i�� 1763<br />
71
H. Ibrahimi, A. Gashi State of knowledge of investigations on <strong>Trichoptera</strong> larvae in Kosova<br />
72<br />
Lepptoceridae<br />
Athripsodes aterrimus ����ph���s�� 1836<br />
Athripsodes cinereus C���is�� 1834<br />
Sericostomatidae<br />
Notidobia ciliaris �i��a���s�� 1761<br />
Sericostoma personatum Ki��y & �p���c���� 1826<br />
���ss ����ai����� s���i��s �� T�ich�p����a w����� �����<br />
i� s���� ��h��� �iv���s ��i��sha Riv����� ���api Riv���<br />
a�� s���� ��h��� s�a������� �iv��� a�� s����a�s��� ��s���y<br />
wi�hi� �������a�� i�v��s�i�a�i��s �f �ac�����������h�s<br />
i�v��������a���s.<br />
<strong>Trichoptera</strong> of Mirusha River<br />
�i��sha Riv��� �asi� is ���ca���� i� w��s����� pa�� �f<br />
K�s�va a�� �h�� ���a�� �������h �f �h�� �iv��� is a����<br />
29 ��. Riv��� p�si�i�� is i�p���a�� ���ca�s�� i� is<br />
placed in dividing line of: Black Sea, Aegean and<br />
���ia�ic ���a ca�ch�����s. ����i��s �� ��a�va�� �f<br />
T�ich�p����a as a pa�� �f �������a�� i�v��s�i�a�i��s �f<br />
�����hic �ac��fa��a w����� ����� �y Gashi �1993�. 10<br />
taxa belonging to three families were identified.<br />
Rhyacophilidae<br />
Rhyacophila nubila Zetterstet, 1840<br />
Rhyacophila sp. �����p vulgaris�<br />
Rhyacophila sp.<br />
Hydropsychidae<br />
Hydropsyche sp �����p guttata�<br />
Hydropsyche sp. �����p pellucidula�<br />
Hydropsyche sp. �����p instabilis�<br />
Hydropsyche sp.<br />
Limnephilidae<br />
Limnephilidae ����. sp<br />
Stenophylax sp.<br />
Potamophylax sp.<br />
Conclusions<br />
I�v��s�i�a�i��s �� T�ich�p����a i� K�s�va a��� �����a�iv����y<br />
���w a�� i�c��p�������. B��si��� v���y f��w ����ai����� s���i��s��<br />
�h�� i�v������i��s a��� ��s���y a ���s���� �f �������a�� i�v��s�i-<br />
�a�i��s �� �����hic �ac��i�v��������a���s. Th��s�� fa�i��i��s<br />
of <strong>Trichoptera</strong> are identified in larval stage so far in<br />
these studies: Rhyacophilidae, Glossosomatidae,<br />
Phi���p��a�i�a���� P���yc������p��i�a���� Hy���psychi�a����<br />
�i����phi��i�a���� G����i�a���� ���pi��s���a�i�a����<br />
B�achyc�����i�a���� O�����c���i�a���� ���p��c���i�a�� a��<br />
����ic�s���a�i�a��. O���i�� s���i��s a��� �� �h�� p��c��ss<br />
i� �i��ica Riv����� P�ish�i�a Riv��� a�� s��v���a�� ��h���<br />
s����a�s a�� �iv���s�� a�� �h��y sh�w p���s���c�� �f v���y<br />
�ich T�ich�p����a fa��a.<br />
Th����� a��� i������i��s �� c���i���� f���h��� wi�h �h��s��<br />
s���i��s i�c����i�� a����� s�a���s �f T�ich�p����a i�<br />
�h�� ���a� f������.<br />
References<br />
�v�y��i�� B. 1988 - Rasprostranjenje ličinki <strong>Trichoptera</strong><br />
u bentosu izvorišnog područja Bijelog Drima,<br />
�a�is�a�s�i �a��� P�i����� �a����a�ic�i Fa����������<br />
Za������� 3 - �2.<br />
Gashi, A. 1993. - Prostorna i sezonska distribucija<br />
makrozoobentosa u Rijeci Mirusa- Magistarski<br />
�a��� P�i����� �a����a�ic�i Fa���������� Za������� 4-60.<br />
K����i - G�apci�� �. 2002. - H������i�i i �a���fa��ës<br />
së ������si� �ë ��j���hë� �� ����i� D�i�i i<br />
Ba��hë �h�� ����i i saj �ë �is��i��i�i� �� �����j��v�� �ë<br />
p��shqv�� Salmo trutta fario �. �h�� Barbus barbus<br />
�.�� Fa��������i i �h����cav�� �a����a�i��-Na�y�������<br />
P�ish�i�a�� 1 - 82.<br />
Ra��va��vic�� �.1931. - R��������a�i ispi�iva�ja<br />
�a���a�s�ih ��ih�p����a.- G��. J���s��. E����.<br />
D��s�va�� �-6�� 1�9- 192.<br />
Shkukriu, A. 1979. - Ekoloska uvjetnost i zonalni<br />
raspored makrozoobentosa u rijeci Prizrenska<br />
Bistrica- Doktorska disertacija, Prirodno Matematicki<br />
Fakultet, Zagreb, 6 - 124.<br />
<strong>Ferrantia</strong> • 55 / 2008
O. Kiss The <strong>Trichoptera</strong> (Insecta) of the Bán Stream, Bükk Mts., northern Hungary<br />
The <strong>Trichoptera</strong> (Insecta) of the Bán Stream,<br />
Bükk Mts., northern Hungary<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Ottó Kiss<br />
K���y Es������h�y C����������<br />
D��pa������� �f Z������y<br />
3300 E������ ���á�y�a �. 6.�� H���a�y<br />
Keywords: caddis larvae, Bán stream, water quality, functional feeding groups, Hungary<br />
Abstract<br />
Larvae of <strong>Trichoptera</strong> were collected monthly at five<br />
sa�p��i�� si���s a����� �h�� Bá� s����a� f��� �p�i�� �� ��a���<br />
���p���������� 2004. Th�� physica���� ch���ica�� a�� �i�����ica��<br />
pa�a�������s as w������ as �h�� ������aphic ���sc�ip�i�� �f �h��<br />
sa�p��i�� si���s a��� �iv���. Th�� �����i���i�a�� �is��i���i�� �f<br />
��a�va�� a����� �h�� ���c�������� hyp�c������ a�� ��pi�hi�h���<br />
Introduction<br />
Ea���i��� �a�a �� �h�� T�ich�p����a fa��a �f �h�� Bá�<br />
Va������y i� �h�� Bü�� �����ai�s w����� p����ish��� �y<br />
�á���i �1938�� 1939��� Ujh����yi �1974� a�� Nó��á�i ���<br />
a��. �1996�. Th�� ��j��c�iv�� �f �y i�v��s�i�a�i��s was<br />
pa����y �� c����i����� �� �h�� ����ai����� ���w�������� �f<br />
�h�� fa��a �y s��v��yi�� �h�� ��a�va�� ass������a���s �f<br />
T�ich�p����a a�� �h�� acc��pa�yi�� fa��a�� �����������s<br />
a�� pa����y �� i�c������ s���� a��i�i��a�� vi��wp�i��s��<br />
such as the differentiation of the longitudinal<br />
����c�������� hyp�c�������� ��pi�hi�h���� ������s �f �h��<br />
stream – as made for other streams of the Bükk<br />
�����ai�s �Kiss 1977a�� 1978 1979�� 1982-83�� 1984a��<br />
1984��� 1987�� 1991a�� 2002; Kiss & �ch����a 1996; Kiss<br />
��� a��. 1998�� 1999�� 2000a�� 2003; �ch����a 1999�� 2004;<br />
Schmera & Kiss 2000) – and the assessment of the<br />
ch���ica�� a�� �i�����ica�� wa���� q�a��i�y �f �h�� s����a�<br />
������s as w������ as f��c�i��a�� f�����i�� ����p c��p�si�i��<br />
�f �h�� c�������c���� ��ich�p����a� sp��ci��s a��� p���s�������. B��h<br />
�h�� ch���ica�� a�� �i�����ica�� wa���� q�a��i�y ass��ss�����s<br />
revealed the water of the spring and the first order<br />
s��c�i�� �f �h�� s����a� ���i�� �f q�a��i�y c��ass ������ i.��.<br />
��i��i�� wa���� q�a��i�y.<br />
s��c�i�� s���i����� ������s��a�i�� �h�� i�p���a�c�� �f<br />
���vi��������a�� p�����c�i�� �f �his a���a.<br />
Material and methods<br />
The study area (B1-B5: sampling sites, Fig. 1) is<br />
���ca���� a� ������va�i��s �f 310-�28 � a� 48 � 06’N a��<br />
20 � 28’E�� N �f Bá��vá�y p��a� �� �h�� ����h���� ������ �f<br />
�h�� Bü�� p��a���a� i� �h�� Bü�� �����ai�s�� H���a�y.<br />
Fiv�� sa�p��i�� si���s w����� ch�s��� wi�hi� �h�� � ��<br />
����� 1 s� ������ s��c�i�� �f �h�� s����a��� s�a��i�� f���<br />
�h�� sp�i��. �� a � �� �is�a�c�� f��� �h�� sp�i����<br />
wh����� �h�� Bá� s����a� �a���s a NE ������ �h�� ���i��vás<br />
stream flows into it, and from this point the Bán<br />
s����a� ca� ��� c��si������� as 2 �� ������ s����a�. Th��<br />
������aphica�� p�si�i��s w����� ��������i���� wi�h a<br />
73
O. Kiss The <strong>Trichoptera</strong> (Insecta) of the Bán Stream, Bükk Mts., northern Hungary<br />
74<br />
Fig. 1: Map of study area with sampling sites (B1-5).<br />
<strong>Ferrantia</strong> • 55 / 2008
O. Kiss The <strong>Trichoptera</strong> (Insecta) of the Bán Stream, Bükk Mts., northern Hungary<br />
Ga��i� �yp�� GP�. E�p����a���y ���as���������s �f<br />
ch���ica�� pa�a�������s w����� �a���� wi�h a �����i��i���<br />
P4 �yp�� ������c��������ic ���vic��. Th�� ca��is ��a�va�� a��<br />
�h�� acc��pa�yi�� fa��a�� �����������s w����� sa�p�����<br />
����h��y f��� �p�i�� �� ��a��� ���p�������� 2004�� �si��<br />
�h�� ����h��s �f Ka������ & Ri������� �1960� a�� �aca�<br />
�19�8�.<br />
The imagines were caught by netting along the<br />
s����a�.<br />
For the identification of the trichopteran larvae<br />
Wa�i����� & G�af �1997� a�� Hic�i� �1967� w�����<br />
used. The trichopteran imagines were identified<br />
�si�� �a��ic�y (1983). For the identification of<br />
�h�� ��h��� �ac��i�v��������a���s �h�� H���a�ia�<br />
��a�s��a�i�� �f Bäh��a�� �2000� a�� �h�� w���<br />
�f Pöc��� �1988� w����� �s���. Dip����a ��a�va�� w�����<br />
identified at family level, based on Biró (1981).<br />
Results and discussion<br />
R��s����s a��� s���a�i����� i� Ta�. 1.<br />
Sampling site B1, a 2 �� 4 � ����� s��c�i�� �f �h��<br />
sp�i�� ����i�� ����i��i�� wi�h �h�� �h���c������ �a�s�<br />
sp�i�� a� a� ������va�i�� �f �28 � a� 48 � 06’N a��<br />
20 � 28’E�� is ���ca���� wi�hi� ��ay���s �f �i������ T�iassic<br />
��i���s�����.<br />
Th�� wa���� ����p���a����� �a���� is 8.0-8.7 � C�� �h�� pH<br />
va�����s va�y ����w����� 6.86 a�� 7.7�� c����c�ivi�y is<br />
480 µS/cm and the dissolved oxygen concentration<br />
is 9.2 ��/�� �83.1%�. Th�� h������a�s �Carpinus<br />
betulus �.� p��vi��� s�ch a ����s�� ca��py ���a� �h��<br />
sp�i�� �ha� �h�� a���a is f�����y sha����. Th�� wi��h �f<br />
�h�� sp�i�� ����i�� is �0-60 c� wi�h ��a���� s�����s as<br />
bottom substrate. It is a typical eucrenon region.<br />
�a�va�� �f Rhyacophila fasciata Ha������ 18�9�� Agapetus<br />
fuscipes C���is�� 1834 and Ecclisopterix madida<br />
�c�ach��a��� 1867 w����� c�������c���� a� �his si���. Th��<br />
���i�a�� �����������s �f �h�� acc��pa�yi�� fa��a<br />
w����� Crenobia alpina Da�a , Sadleriana pannonica<br />
Frfl. and Gammarus fossarum K�ch.<br />
Sampling site B2 is si��a���� 400 � ��w�s����a���<br />
a� a� ������va�i�� �f 498 �. I� is a hyp�c������ ������<br />
of the first order stream section with high velocity<br />
wa���� ��shi�� ��w� a �a��� a�� c���i��i�� i�s way<br />
swiftly over the large stones of the streambed. The<br />
s����a� wi��h ������a�h �h�� �a� is 180 c��� wa����<br />
���p�h is 7 c�. I� is a ha��f-sha���� a���a wi�h s���y<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
s��s��a���. B��y��� �h�� �a��� �h�� s����a����� wi����s<br />
and is covered with fine sediments. On the banks,<br />
�h�� v������a�i�� c��sis�s �f Petasitetum hybridi D�s�<br />
and common nettle (Urtica dioica �.�. Th�� wa����<br />
����p���a����� �a���� is ����w����� 9.0 � C a�� 10.3 � C��<br />
�h�� pH is 8.34�� c����c�ivi�y �a����s f��� 471 �� 477<br />
µS/cm and the dissolved oxygen concentration is<br />
8.�� ��/�� �77.2 %�. Rhyacophila fasciata, Rhyacophila<br />
pubescens Pic������ 1834 a�� Agapetus fuscipes w�����<br />
���i�a�� a���� �h�� s��v��� ��ich�p����a� sp��ci��s<br />
c�������c���� h�����. �a�va�� �f Wormaldia occipitalis<br />
Pic������ 1834 w����� �a���. Th�� ���i�a�� �����������s �f<br />
�h�� acc��pa�yi�� fa��a w����� Crenobia alpina a��<br />
Sadleriana pannonica�� a���h���h Chi�����i�a�� a��<br />
�i����i�a�� ��a�va�� w����� a��s� c������� ��v��� Gordius<br />
aquaticus �. �cc������.<br />
Sampling site B3 is si��a���� a���� 4�0 � f��� �h��<br />
sp�i�� a�� ��w�s����a� �f a ��i���� a� a� ������va�i��<br />
�f 478 �. H������� �h�� s����a� wi��h is 100 c��� �h��<br />
water depth is 8 cm, the bottom substrate consists<br />
of large stones, and the water is fast-flowing. On the<br />
ha��f-sha���� �a��s�� c����� a������ �Alnus glutinosa<br />
�. Ga���.� a�� s�a��s �f Petasitetum hybridi D�s�<br />
a��� f����. Th�� wa���� ����p���a����� �a����s ����w�����<br />
9.2 � C a�� 10.� � C�� �h�� pH is 8.3�� c����c�ivi�y<br />
is 467-468 µS/cm and the dissolved oxygen<br />
c��c�����a�i�� is 8.77 ��/�� �79.2%�. Of �h�� s��v���<br />
sp��ci��s �f T�ich�p����a c�������c������ �h�� ���i�a��<br />
����s w����� Rhyacophila fasciata, Agapetus fuscipes��<br />
a�� Ecclisopteryx madida. Th�� acc��pa�yi��<br />
fa��a was ���p���s������� �y Crenobia alpina, Dugesia<br />
gonocephala D��. a�� Sadleriana pannonica.<br />
Sampling site B4, app���i�a�����y 800 �<br />
downstream of the spring and after a roadbend,<br />
is ���ca���� a� a� ������va�i�� �f 474 �. Th�� �i�h�<br />
bank of the streambed is boggy, its left bank is<br />
steep. The bottom substrate ranges from small<br />
sections of large and small stones to sand and fine<br />
s���i����� acc�����a�i��s. Th�� a���a is f�����y sha����<br />
�y h������a� �Carpinus betulus �.� a�� c�����<br />
a������ �Alnus glutinosa �. Ga���.�. Thic� s�a��s<br />
�f Urtica dioica �.�� Petasitetum hybridi D�s��� a��<br />
Sambucus nigra �. a��� f����. Th�� s����a� wi��h<br />
va�i��s f��� 8� �� 120 c��� �h�� wa���� ���p�h is 8-9<br />
cm. The water temperatures fluctuate between<br />
9.� � C a�� 11.1 � C�� �h�� pH is ����w����� 6.�� a��<br />
8.3, conductivity is between 456 µS/cm and 484<br />
µS/cm and the dissolved oxygen concentration<br />
is 8.�6 ��/�� �78.2%�. Of �h�� ���� sp��ci��s f����<br />
h����� �h�� ���i�a�� ����s w����� Agapetus fuscipes��<br />
Hydropsyche instabilis C���is�� 1834�� a�� Ecclisopteryx<br />
75
O. Kiss The <strong>Trichoptera</strong> (Insecta) of the Bán Stream, Bükk Mts., northern Hungary<br />
76<br />
Tab. 1: Zonal distribution of the trichopteran larvae and the accompanying fauna in a 3.6 long section<br />
of the Bán stream, Bükk Mts; functional feeding groups of the trichopteran larvae; water quality<br />
indices of the trichopteran species of the Bán stream given by Moog (1995). Legend: �=1- �=1- =1-<br />
2 specimens, ��=3-6 ��=3-6 =3-6 specimens, ���= ���= ���= ���= = over over 6 6 specimens; specimens; sh=shredders, sh=shredders, =shredders, c=collectors, c=collectors, c=collectors, f=filterers,<br />
f=filterers,<br />
f=filterers,<br />
p=predators, d=detritivores, h=herbivores; x=xenosaprobic, o=oligosaprobic, β=beta-meso- -mesomesosaprobic, α=alpha-mesosaprobic, p=polysaprobic.<br />
Species of the trichopteran larvae<br />
Eucrenon<br />
Sampling sites Func-<br />
Hypocrenon<br />
Epirhithron<br />
Species of the accompanying fauna<br />
N���a�h�����i��h��s/T���������a�ia<br />
C������ia a��pi�a *** *** ***<br />
D����sia ����c��pha��a * *** ***<br />
N���a�����pha<br />
G���i�s aq�a�ic�s * * *<br />
Pa�ach�������s �����sa��s *<br />
Gas���p��a<br />
P��a����a�i�s c������s * *<br />
�a������ia�a pa����ica *** *** *** *** ***<br />
C��s�ac��a/��phip��a<br />
Ga��a��s f�ssa��� *** *** *** *** ***<br />
Dip����a<br />
Chi�����i�a�� ** ** ** **<br />
Tip���i�a�� * *<br />
�i����i�a�� ** ** **<br />
Tha��a����i�a�� *<br />
Di�i�a�� *<br />
����is��c���i�a�� *<br />
tional<br />
feeding<br />
Water quality<br />
B1 B2 B3 B4 B5 groups x o β α p<br />
1 Rhyac�phi��a fascia�a *** *** *** *** *** p 2 4 4<br />
2 Rhyac�phi��a ����i����a�a * ** * ** p 4 6<br />
3 Rhyac�phi��a p����sc���s *** *** *** p 7 3<br />
4 Rhyac�phi��a ��is�is * * p 2 3 4 1<br />
� ��ap����s f�scip��s *** *** *** *** *** s 4 � 1<br />
6 �y�a�ap����s ��s����yi * * s 8 2<br />
7 W���a���ia �ccipi�a��is ** c��f 8 2<br />
8 �i��� pa����ip��s * s 1 4 �<br />
9 P����c���c����ia c��sp���sa ** ** ** ** p 1 3 4 2<br />
10 Hy���psych�� i�s�a�i��is *** *** c��f ��p 1 4 � +<br />
11 Hy���psych�� p�������ci����a * ** c��f�� p 2 � 3<br />
12 Ha����s�s �i�i�a��s ** sh�� h � 4 1<br />
13 Ecc��is�p����y� �a�i�a *** *** *** *** sh�� � 4 4 2<br />
14 G�a����a���i�s �i�i��s * * sh�����p - - -<br />
1� P��a��phy��a� ������ip����is ** s�� � 4 4 2<br />
16 ������phy��a� p����is��s * s�� � - + +<br />
17 Limnephilus a���nis ** s�� ��� h - + +<br />
18 �i����phi���s ����a��s * s�� ��� h + +<br />
19 Limnephilus vittatus * s�� ��� h + +<br />
20 ����ic�s���a p���s��a��� ** ** s 3 4 3<br />
21 O�����c����� a���ic����� ** s�� ��� h 1 6 3<br />
<strong>Ferrantia</strong> • 55 / 2008
O. Kiss The <strong>Trichoptera</strong> (Insecta) of the Bán Stream, Bükk Mts., northern Hungary<br />
madida. T�ich�p����a� ��a�va�� wi�h a p���f������c�� f��<br />
����ic wa����s c��p�is��� Rhyacophila tristis Pic������<br />
1834 �a s��a��pi��� sp��ci��s��� Rhyacophila fasciata��<br />
Odontocerum albicorne �c�p���i�� 1763�� Hydropsyche<br />
instabilis, Plectrocnemia conspersa C���is�� 1834 a��<br />
Ecclisopteryx madida. I� a��i�i���� ��a�va�� wi�h a<br />
p���f������c�� f�� ������ic wa����s w����� sa�p������� ��.�.<br />
Halesus digitatus �ch�a���� 1781 a�� Potamophylax<br />
rotundipennis B�a������ 18�7. Wi�h ���sp��c� �� �h��<br />
acc��pa�yi�� fa��a�� Dugesia gonocephala was<br />
c������� ��� Gordius aquaticus a�� Tip���i�a��<br />
��a�va�� a��s� �cc������.<br />
Sampling site B5�� 3600 � ��w�s����a� �f �h��<br />
sp�i���� is si��a���� ���a� �h�� �ai����a�-c��ssi��<br />
wh����� �h�� va������y wi����s a� a� ������va�i�� �f 310<br />
� a��v�� s��a ����v���� a� 48 � 08’N a�� 20 � 27’E. �� �h��<br />
sa�p��i�� si��� �h�� s����a� wi��h is 1�0 c� a��<br />
�h�� wa���� ���p�h is 9 c�. Th�� �a��s a��� sha����<br />
�y Petasitetum hybridi D�s��� Sambucus nigra �.<br />
a�� Carpinus betulus �. Th�� wa���� ����p���a�����s<br />
fluctuate from 9.5 � C �� 14.1 � C�� �h�� pH va����� is<br />
8.42, the conductivity ranges from 456 µS/cm to<br />
484 µS/cm and the dissolved oxygen concentration<br />
is 8.72 ��/�� �87.7%�. Of �h�� 19 ��ich�p����a� sp��ci��s<br />
c�������c���� h����� �h�� ���i�a�� ����s w����� Rhyacophila<br />
fasciata�� Agapetus fuscipes�� Hydropsyche instabilis��<br />
a�� Ecclisopteryx madida. �����a�� ����ic sp��ci��s<br />
c��p�is��� Odontocerum albicorne�� Hydropsyche<br />
instabilis, Ecclisopteryx madida, Agapetus fuscipes,<br />
Rhyacophila fasciata�� a�� Rhyacophila tristis�� ���<br />
Halesus digitatus, a ������ic sp��ci��s�� was a��s� f����.<br />
I� a��i�i���� Dugesia gonocephala, Parachordodes<br />
tolosanus D�j. a�� Megistocera sp. �Dip����a� w�����<br />
c�������c����.<br />
� ���a�� �f 226 i��ivi��a��s ��������i�� �� 21 sp��ci��s �f<br />
T�ich�p����a w����� c�������c������ ������h��� wi�h 6 sp��ci��s<br />
�f Dip����a�� �w� sp��ci��s �f N���a�h�����i��h��s/<br />
T���������a�ia�� �w� sp��ci��s �f N���a�����pha��<br />
�w� sp��ci��s �f Gas���p��a�� a�� ���� sp��ci��s �f<br />
C��s�ac��a/��phip��a �Ta�. 1�. This sp��ci��s<br />
i�v������y is �ypica�� f�� �h�� fa��a�� c��p�si�i�� �f<br />
a 1 s� ������ s����a� i� a �ypica�� �����ai� �a���� �f<br />
����i�� h��i�h�. �p��ci��s �ich���ss a�� a����a�c��<br />
i�c���as�� ��w�s����a� f��� �h�� sp�i�� ���� ��<br />
�h�� va�i��� s��s��a���s a�� �h�� avai��a�i��i�y �f a<br />
wi���� �a���� �f f��� ���s���c��s. I� wi������� �h��<br />
s����a� is ��� f������� ���� �� �h�� a����s� c��s�a��<br />
wa���� ����p���a����� a�� p��vi���s s�i�a����� ��ivi��<br />
c���i�i��s f�� �h�� �����hic c�����i�i��s.<br />
Th�� cha�ac����is�ic ��ich�p����a� sp��ci��s w�����<br />
Rhyacophila tristis a�� Rhyacophila pubescens,<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Wormaldia occipitalis, Agapetus fuscipes a��<br />
Ecclisopteryx madida. O�h��� cha�ac����is�ic<br />
�ac�����������hic �����������s c��p�is��� Crenobia<br />
alpina, Sadleriana pannonica�� a�� Parachordodes<br />
tolosanus.<br />
Fuctional feeding groups (Tab. 1)<br />
����h���h �h�� �aj��i�y �f �h�� ��ich�p����a� ��a�va��<br />
a��� c�������c���s�� ���� sp��ci��s �f �h�� ca��is ��a�va�� i� �his<br />
s���y a���a w����� sh��������s�� f�����i�� �� �ac��phy���s<br />
a��/�� CPO�. Th����� sp��ci��s�� Wormaldia occipitalis<br />
a�� y���� i�s�a�s �f Hydropsyche instabilis a��<br />
Hydropsyche pellucidula C���is�� 1834 �������� ��<br />
the group of filtering collectors, with FPOM as<br />
�h��i� �ai� f��� ���s���c��. Th����� sp��ci��s�� Agapetus<br />
fuscipes�� Synagapetus moselyi U�������� 1938 a�� Silo<br />
pallipes Fa��ici�s�� 1781�� ���p���s������� �h�� sc�ap���s.<br />
P����a���s w����� ���p���s������� �y a �����a�iv����y<br />
large number of species: 4 Rhyacophila sp��ci��s��<br />
���� Plectrocnemia sp��ci��s a�� �h�� ��a�va�� �f �w�<br />
Hydropsyche sp��ci��s f��� i�s�a� 3 ��wa��s.<br />
Water quality<br />
Bas��� �� �h�� ch���ica�� pa�a�������s a�� i�<br />
compliance with the qualification specifications<br />
�D�vai ��� a��. 1992; �KO�Z. 1989� i� ca� ��� s�a����<br />
�ha� �h�� wa���� i� �h�� 3600 � ����� ���ach �f �h�� Bá�<br />
stream is of first class, i.e. of drinking water quality.<br />
I� �ac��i�v��������a���s�� �h�� f���q����cy va�����s �f<br />
�h�� T�ich�p����a�� Gas���p��a a�� ��phip��a a���<br />
of special significance in the different saprobic<br />
ca������i��s f�� �h�� ass��ss����� �f �h�� �i�����ica��<br />
wa���� q�a��i�y ����� 199��. ����h���h s��v���a��<br />
i��ica��� sp��ci��s �f T�ich�p����a acc�����a��� i�<br />
�h�� sa��� sap���ic ca������y�� �h��y a��s� �cc�� i�<br />
��h��� sap���ic ca������i��s �Kiss ��� a��. 2002�. T���<br />
��ich�p����a� sp��ci��s wi�h hi�h f���q����cy va�����s<br />
�4 �� �v��� 4� i��ica��� ���i��sap���ic wa����s. �i�<br />
�f �h��s�� 10 sp��ci��s �v�����ap wi�h 6 �f 9 i��ica���<br />
species with high frequency values in the β-<br />
���s�sap���ic ca������y. Fiv�� i��ica��� sp��ci��s��<br />
�h����� �f �h��� wi�h �a�h��� hi�h va�����s �7-8��� p���f���<br />
�����sap���ic wa����s. ���v���a�� sp��ci��s wi�h ���w<br />
f���q����cy va�����s �1-3� �cc�� i� a���� f��� sap���ic<br />
ca������i��s �Ta�. 1�.<br />
Bas��� �� �h�� �i�i��ica��� sp��ci��s w�� s�a��� �ha� �h��<br />
biological water quality is of first class, i.e. it is in<br />
acc���a�c�� wi�h �h�� ch���ica�� wa���� q�a��i�y.<br />
77
O. Kiss The <strong>Trichoptera</strong> (Insecta) of the Bán Stream, Bükk Mts., northern Hungary<br />
78<br />
These findings indicate the importance of nature<br />
c��s���va�i�� a�� ���vi��������a�� p�����c�i�� �f �h��<br />
s����a� wi�hi� �h�� Bü�� Na�i��a�� Pa��.<br />
Acknowledgements<br />
Th�� ���i�is��a�i�� �f �h�� Bü�� Na�i��a�� Pa�� is<br />
�ha����� f�� �ivi�� p����issi�� �� i�v��s�i�a��� �h��<br />
s���y a���a.<br />
References<br />
Bäh��a�� R. 2000. - G���i�c�������� á����a��� ha�á����ója.<br />
Mezőg. Kiadó, Budapest �i� H���a�ia���� 383 p.<br />
Bi�ó K. 1981. - ��� á�vas��ú�y�� ��á�vá� �Chi����-<br />
�i�a��� �isha�á����ója. Vízdok. 11: 1-230.<br />
Hic�i� N. E. 1967. – Caddis Larvae. Larvae of the<br />
B�i�ish T�ich�p����a. H��chi�s�� �f �������� 4�3 p.<br />
D�vai Gy.�� Dévai I. & Wittner I. 1992. - A vízminőség<br />
f��a���������s���������� ���y á�f��ó ���c��pciója.<br />
3. rész. Az ökológiai vízminőség jellemzésének<br />
lehetőségei. Acta Biol. Debr. Suppl. Oecol.<br />
Hung. 4: 49-185.<br />
Ka������ �. & Ri������� W. 1960. - Method for Quantitative<br />
Study of the Bottom Fauna of Tatra<br />
Streams. Polsch. Hydrol. 8: 9�-10�.<br />
Kiss O. 1977. - O� �h�� T�ich�p����a fa��a �f �h�� Bü��<br />
Mountains, N. Hungary: 89-101, in Crichton<br />
�.I. ������� P��c�����i��s �f �h�� 2 �� I������a�i��a��<br />
�y�p�si�� �� T�ich�p����a�� U�iv���si�y �f<br />
R��a�i���� E����a���� D�. W. J��� B.V. P����ish���s��<br />
Th�� Ha����.<br />
Kiss O. 1977�. - A „mosaic-pattern” elv bemutatása<br />
a Bü�� h���ys��i ���a��aj�a pa�a������s�����<br />
T�ich�p����ái�. �P���s����a�i�� �f �h�� „��saicpattern”<br />
principle on the <strong>Trichoptera</strong> of the<br />
s����a� sys���� ���a��aj�a i� �h�� Bü�� �����ai�s�.<br />
Folia Hist.-nat. Mus. Matraensis 4: 63-69.<br />
Kiss O. 1978. - � Bü�� h���ys��i Dis���ós�ú� �s<br />
Sebesvíz <strong>Trichoptera</strong> együtteseiről. (On the<br />
T�ich�p����a c�����i�i��s �f �h�� �i���� Dis���ós�ú�<br />
a�� s����a� ������sví�� i� �h�� Bü�� �����ai�s�.<br />
Acta Acad. Paed. Agriensis, Nova Series 14:<br />
493-�07.<br />
Kiss O. 1979. - � f���yóví��i �á�s���ás�� ����ai�<br />
����v����� �������������s�� �s a�� ö����ó�iai �ich��. �Th��<br />
interpretation of the mosaic-pattern principle<br />
�f �h�� ass�cia�i��s i� s����a�s a�� �h�� ��c����-<br />
�ica�� �ich���. �c�a �ca�. Pa���. ���i���sis�� N�va<br />
Series 15: 453-466.<br />
Kiss O. 1982-83. - � s���y �f �h�� T�ich�p����a �f �h��<br />
���a��aj�a Va������y ���a� ���i��vásvá�a� as i��ica����<br />
�y ��i�h� ��ap �a����ia��. F���ia His�.-�a�. ��s.<br />
�a��a���sis 97-106.<br />
Kiss O. 1984a. - Fénycsapdával gyűjtött Trichopterák<br />
a Bükk hegységi Vöröskő-völgyből.<br />
�T�ich�p����a c�������c���� �y ��i�h�-��ap f���<br />
Vöröskő-Valley in the Bükk Mountains). Acta<br />
Acad. Paed. Agriensis, Nova Series 17: 709-<br />
718.<br />
Kiss O. 1984b. - <strong>Trichoptera</strong> in an intermittent rill of<br />
the Bükk Mountains, North Hungary: 191-195,<br />
i� ���s�� J. C. ������� P��c�����i��s �f �h�� 4 �h I�����-<br />
�a�i��a�� �y�p�si�� �� T�ich�p����a�� C�����s����<br />
����h Ca����i�a�� D�. W. J��� P����ish���s�� Th��<br />
Ha����.<br />
Kiss O. 1987. - � Bü�� h���ys��i Na�y-vö���y<br />
(Nagyvisnyó) fénycsapdával gyűjtött Trichop-<br />
����ái. �T�ich�p����a c�������c���� wi�h a ��i�h�-��ap<br />
f��� �h�� Na�y-Va������y �Na�yvis�yó� i� �h��<br />
Bü�� �����ai�s�. �c�a �ca�. Pa���. ���i���sis��<br />
Nova Series 18: 3-8.<br />
Kiss O. 1991a. - A Bükk hegységi Ablakoskő és<br />
Nagy-völgy <strong>Trichoptera</strong> lárva-együttesei.<br />
(<strong>Trichoptera</strong> larvae from the Ablakoskő and<br />
Na�y-Va������y �f �h�� Bü�� �����ai�s�. �c�a<br />
Acad. Paed. Agriensis, Nova Series 20: 17-36.<br />
Kiss O. 1991�. - T�ich�p����a f��� a ��i�h� ��ap i�<br />
�h�� Bü�� �����ai�s�� N���h H���a�y�� 1980-<br />
1988: 233-236, in Tomaszewski C. (ed), Procee-<br />
�i��s �f �h�� 6 �h I������a�i��a�� �y�p�si��<br />
�� T�ich�p����a�� ��-Za��pa����� P���a����<br />
�ic�i��wic�� �. U�iv���si�y P���ss�� P����a�.<br />
Kiss O. & �ch����a D. 1996. - Die Köcherfliegen<br />
der Quellregionen des nord-ungarishen Bü��<br />
Gebirge. Crunoecia 5: 67-70.<br />
Kiss O.�� Lőrincz G. & �i��s �. 1998. - � Bü��<br />
h���ys��i H�ss��ú-vö���y T�ich�p����ái.<br />
�T�ich�p����a �f �h�� H�ss��ú-Va������y �f �h�� Bü��<br />
�����ai�s�. �c�a �ca�. P���. ���i���sis�� N�va<br />
Series 27: 1�-33.<br />
<strong>Ferrantia</strong> • 55 / 2008
O. Kiss The <strong>Trichoptera</strong> (Insecta) of the Bán Stream, Bükk Mts., northern Hungary<br />
Kiss O.�� ����i��vics �.�� ���i����vá�i G. & Fis��i I.<br />
1999. - T�ich�p����a f��� a ��i�h� ��ap ���a� �h��<br />
Eger brook at Szarvaskő (Bükk Mountains,<br />
North Hungary): 165-170, in Malicky H. &<br />
Cha��a�a�������� P. ����s��� P��c�����i��s �f �h��<br />
9 �h I������a�i��a�� �y�p�si�� �� T�ich�p����a��<br />
Fac����y �f �ci���c���� U�iv���si�y �f Chia�� �ai��<br />
Thai��a��.<br />
Kiss O.�� ���y��ósi �. & �ch����a D. 2000a. - �<br />
Bü�� h���ys��i Ha�á� ��ápa �s Tá��á�yi pa�a�<br />
T�ich�p����a ��á�va �á�s���ásai. ���saic-��i���<br />
pattern association of <strong>Trichoptera</strong> larvae of two<br />
�����s i� �h�� Bü�� �����ai�s�. Hi�����ó�iai<br />
Közlöny 5-6: 362-363.<br />
Kiss O. & ����i��vics �. 2000�. - F��c�i��a��<br />
f�����i�� ����ps a����� a ���w��a�� s����a� �E����<br />
s����a��� H���a�y�. V���h. I������a�. V�����i�.<br />
Limnol. 27: 1489-1493.<br />
Kiss O. 2002. - T�ich�p����a c�����i�i��s �f a Ri����<br />
and a Stream in the Bükk Mts. (north Hungary):<br />
�37-�43�� i� ���y W. ������� P��c�����i��s �f �h��<br />
10 �h I������a�i��a�� �y�p�si�� �� T�ich�p����a��<br />
P��s�a��� G����a�y�� G���c��� & Ev���s�� K���������.<br />
Kiss O.�� Vi��i�i �. & F��h�� I. 2002. - Th�� wa����<br />
q�a��i�y s�a��� �f �h�� ���a��aj�a �����a��� Bü�� ��s.��<br />
Hungary. Braueria, <strong>Trichoptera</strong> Newsletter 29:<br />
31-34.<br />
Kiss O.�� F��h�� I. & �ch����a D. 2003. - Cha�ac-<br />
����is�ics �f ca��is ��a�va�� ass������a���s f���<br />
sha�����w ��a���s i� �h�� Bü�� ��s.�� ����h H���a�y.<br />
Hydrobiologia 506-509: 365-372.<br />
�aca� T. 19�8. - ����h��s �f �a�p��i�� �h��<br />
Bottom Fauna in Stony Streams. Interna-<br />
�i��a�� �ss�cia�i�� �f Th�������ica�� a�� �pp��i���<br />
�i�������y. C���. 8.<br />
�a��ic�y H. 1983. - ����as �f E���p��a� T�ich�p����a.<br />
D�. W. J��� P����ish���s�� Th�� Ha����-B�s���-<br />
������. 1-298.<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
���� O. ������� 199�. - Fa��a �q�a�ica ��s��iaca.<br />
B�����s�i�is����i�� fü� �a��-��� F��s�wi��schaft,<br />
Wien.<br />
MKOSZ. 1989. - Ivóvíz minősítés fizikai és kémiai<br />
vi��s�á��a� a��apjá�.<br />
Nó��á�i �.�� Kiss O. & Uh�����vich<br />
Uh�����vich Uh�����vich Á. 1996. - Th��<br />
<strong>Trichoptera</strong> fauna of the Bükk National Park:<br />
397-409�� i� �ah���a �. ������� Th�� Fa��a �f �h��<br />
Bü�� Na�i��a�� Pa���� V������� 2�� H���a�ia�<br />
Na���a�� His���y ��s������ B��ap��s�.<br />
Pöc��� �. 1988. - B��s�i�����sch��üss���� fü� P���aca-<br />
�i�a�� ���� ös�������ichisch��� D��a� �C��s�ac��a��<br />
�a��ac�s��aca�. Wasser und Abwasser 32: 89-<br />
111.<br />
�á���i J. 1938. - ��a��� a Bü��-h���ys�� ��va�fa�nájának<br />
ismeretéhez. Állattani Közlemények 1:<br />
�1-61.<br />
�á���i J. 1939. - ��a��� a Bü�� �s a �á��a ��va�fa�nájához.<br />
Állattani Közlemények 3-4: 1�6 -168.<br />
�ch����a D. 1999. - Előtanulmány az Északi-<br />
�ö���ph���ys�� pa�a�jai�a� ��������s �T�ich�p����a�<br />
lárva együtteseiről. Hidrológiai Közlöny 6:<br />
337-338.<br />
�ch����a D. & Kiss O. 2000. - Mintavételezésből<br />
a�ó�ó ��������s��� ��������s��� �T�ich�p����a�<br />
vizsgálata esetében. Hidrológiai Közlöny 5- 6:<br />
383-384.<br />
�ch����a D. 2004. - �pa�ia�� �is��i���i�� a�� c����istence<br />
patterns of caddisfly larvae �T�ich�p����a�<br />
i� a H���a�ia� s����a�. I������a�. R��v. Hy����i���.<br />
1: 51-57.<br />
Újh����yi �. 1974. - ��a��� a Bü�� �s a �á��a h���ys��<br />
tegzesfaunájához. Állattani Közlemények 3-4:<br />
1�6-168.<br />
Wa�i����� J. & G�af W. 1997. - ����as ���� ös�������ichischen<br />
Köcherfliegenlarven. Facultas Universi�ä�sv�����a���<br />
Wi����� 286 p.<br />
79
S. Pauls, T. Lumbsch, P. Haase Glacial refugia of the montane caddisfly Drusus discolor (Rambur, 1842)<br />
80<br />
Glacial refugia of the montane caddisfly<br />
Drusus discolor (Rambur, 1842)<br />
(Extended Abstract)<br />
Introduction<br />
I� c�����a�� E���p�� �h�� �����acy �f �h�� P����is��c�����<br />
ice ages and their effects on the European Biota<br />
hav�� ������ s��j��c� �� ��ch s���y �v��� �h�� ��as�<br />
f��w ���ca���s. ����� ���c������y a p�����h��a �f s���i��s<br />
hav�� f�c�ss��� �� ���a�i�i�� p�p���a�i�� �������ic<br />
structure using a variety of fingerprinting methods<br />
�� i�f��� �h�� P����is��c����� his���y �f E���p��a� sp��ci��s<br />
(see Hewitt 2004a, b; Schmitt 2007 for recent<br />
���vi��ws�. ��s� �f �h��s�� s���i��s hav�� f�c�ss��� ��<br />
�������s��ia�� sp��ci��s a�� hav�� sh�w� �ha� �h����� a���<br />
several common patterns. For many temperate<br />
species examined to date these patterns suggest<br />
P����is��c����� s��viva�� i� c��i�a�ica����y fav���a�����<br />
����i��s �� ���� �� ����� �f �h�� s���h���� E���p��a�<br />
p���i�s���as. � c����� sc���a�i� i� �h�� ��i����a�����<br />
s�����s�s p�s�-���acia�� ���-c�����isa�i�� �f c�����a��<br />
E���p�� wh����� ��fav���a����� c��i�a��� c���i�i��s<br />
p���vai����� �h����h��� ��ch �f �h�� P����is��c����� �s����<br />
Hewitt 2004a, b; Schmitt 2007 for recent reviews).<br />
O�h��� hyp��h��s��s �f P����is��c����� p���sis����c�� hav��<br />
s�����s���� ���acia�� f�i���� sp��ci��s ���.�. Thi������a��<br />
19�0��� ���acia�� �����ic�s ���.�. Thi������a�� 19�0��� a��<br />
Steffen U. Pauls<br />
Senckenberg – Research Institute and Natural History Museum<br />
D��pa������� �f �i�������y a�� C��s���va�i��<br />
C��a���cys��a�� 12<br />
D-63�71 G�����ha�s���<br />
pa���s497@���.������<br />
Th�� Fi����� ��s������ D��pa������� �f Z������y<br />
1400 �. �a��� �h���� D�iv��<br />
Chica���� I� 6060��� U��<br />
H. Thorsten Lumbsch<br />
Th�� Fi����� ��s������ D��pa������� �f B��a�y<br />
1400 �. �a��� �h���� D�iv��<br />
Chica���� I� 6060��� U��<br />
Peter Haase<br />
Senckenberg – Research Institute and Natural History Museum<br />
D��pa������� �f �i�������y a�� C��s���va�i��<br />
C��a���cys��a�� 12<br />
D-63�71 G�����ha�s���<br />
nunatuks (e.g. Merxmüller 1952). These latter<br />
hyp��h��s��s a��� �h���h� �� ��� �������va�� f�� v���y<br />
c����-ha��y sp��ci��s. F�� v���y f��w a������a�� sp��ci��s<br />
c�yp�ic ����h���� ���f��ia hav�� ������ s�����s����.<br />
Th��s�� a��� p�c����s �f ha�i�a� wi�h fav���a�����<br />
�ic��c��i�a���s i� ����i��s wi�h ��h���wis�� ha�sh<br />
c��i�a�ic c���i�i��s i� c�����a�� E���p�� wh�����<br />
s�a���� ���f��ia�� p�p���a�i��s s��viv��� ����vi��w��� �y<br />
����wa�� & �is���� 2001�.<br />
Unfortunately over the years, little attention has<br />
������ �iv��� �� aq�a�ic ���a�is�s. Th����� is a c�i�ica��<br />
��ac� �f ���w�������� i� �his a���a �f s���y as aq�a�ic<br />
organisms are subject to very different physical<br />
c���i�i��s �ha� �������s��ia�� sp��ci��s a�� p���s��a���y<br />
climate change has different effects on aquatic<br />
�ha� �������s��ia�� ��c�sys����s. This is ��sp��cia����y �����<br />
f�� �����ai� s����a�s�� which hav�� p����a�����<br />
turbulent flow and water temperatures, which are<br />
regulated by fluvial regime and highly dependent<br />
on groundwater influx. Based on these ecosystem<br />
c��si����a�i��s a�� �h�� �is��i���i�� �f �������ics<br />
�a��ic�y �1983� p��p�s��� �ha� c����-wa���� �������a����<br />
mountain stream-dwelling caddisfly species may<br />
hav�� s��viv��� �h�� P����is��c����� �� �h�� s���p��s �f<br />
<strong>Ferrantia</strong> • 55 / 2008
S. Pauls, T. Lumbsch, P. Haase Glacial refugia of the montane caddisfly Drusus discolor (Rambur, 1842)<br />
mountains in permanently flowing streams in<br />
c�����a�� E���p��. Th�� hyp��h��sis �f P����is��c�����<br />
s��viva�� is �as��� �� �h�� fac� �ha� �h�� sp��ci��s ca�<br />
s��viv�� ������������y c���� aq�a�ic ha�i�a�s ���ay. If<br />
streams were permanently flowing throughout<br />
�h�� P����is��c����� �h��y w����� ��� hav�� c������� ������w<br />
0°C. Thus cold-tolerant aquatic organisms would<br />
hav�� ������ s��j��c� �� ��ch ����ss s��v����� ����p���a�����<br />
���c���as��s �ha� �h��i� �������s��ia�� c�������pa��s<br />
��a��ic�y 1983; Pa���s�� ����sch & Haas�� 2006�. ����<br />
a���h���h �h��i� p���s����-�ay �is��i���i�� s�����s�<br />
�ha� ����a��� s����a�-�w������i�� i�s��c�s f��� pa��<br />
�f �h�� a������a�� �i������ �h��i� ���ac�i�� �� c��i�a���<br />
change was vastly different: instead of surviving<br />
i� s���h���� E���p��a� ���f��ia�� �h��y si�p��y<br />
moved locally to permanently flowing, turbulent<br />
�����ai� s����a�s i� �h�� c�����a�� E���p��a�<br />
p���i���acia��. �a��ic�y �1983�� 2000� p��p�s��s �h��<br />
�i����-�yp�� �i���a�� �� ����p a���� aq�a�ic sp��ci��s��<br />
which ���ac���� i� �his �a����� �� P����is��c�����<br />
c����i��.<br />
Population structure and glacial refugia<br />
of Drusus discolor<br />
W�� wa����� �� ���s� �his hyp��h��sis �y s���yi��<br />
the phylogeography of a species, which fulfils the<br />
�is��i���i��a�� a�� ��c�����ica�� ���q�i��������s �f a<br />
�i���a�� sp��ci��s. W�� �h�����f���� s���i��� �h�� �������ic<br />
p�p���a�i�� s���c����� a�� phy���������aphy �f �h��<br />
montane caddisfly Drusus discolor ac��ss i�s ����i���<br />
�a���� �Pa���s�� ����sch & Haas�� 2006�. Th�� sp��ci��s<br />
is restricted to cold turbulent flowing streams in<br />
�����ai� ����i��s i� c�����a�� a�� s���h���� E���p��<br />
��ch�i� 19�6; �a��ic�y 1983; Pa���s 2004�. Th��<br />
�is��i���i�� is i�s���a� f��� �h�� Ca��a��ia� ��s i�<br />
����h���� �pai� i� �h�� s���hw��s� �� �h�� ����h����<br />
Rh���pi ��s i� B����a�ia i� �h�� s���h��as�. Pa���s��<br />
����sch & Haas�� �2006� s���i��� sa�p����s<br />
f��� 71 p�p���a�i��s spa��i�� �h�� ����i��� �a����<br />
a�� �������a���� a�� a�a��ys��� �i��ch����ia��<br />
s��q����c�� �a�a �cy��ch����� ��i�as�� I�� ��COI�<br />
f�� 2�4 i��ivi��a��s. P�p���a�i�� �������ic a��<br />
phy���������aphic a�a��ys��s i�c������� Bay��sia�<br />
�H�����s������c� ��� a��. 2001� a�� s�a�is�ica�� pa�si���y<br />
�T���p��������� C�a��a���� & �i�� 1992; C�����������<br />
P�sa�a & C�a��a���� 2000� phy����������ic i�f������c��s��<br />
�� a�a��ys�� �����a�i��ships ����w����� hap����yp��s a��<br />
hap����yp�� �is��i���i��; a�a��ysis �f ������c���a�<br />
va�ia�c�� ���OV�� �� pa��i�i�� ���a�� ��s���v���<br />
variation among different geographic hierarchies<br />
(Exco���er, Smouse & Quattro 1992); estimates of<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
F ST �W�i�h� 19�1� a�� ���ac� ���s�s �f p�p���a�i��<br />
differentiation (Raymond & Rousset 1995) to<br />
���v��a�� p�p���a�i�� �������ic s���c�����; ���s�s �f<br />
s������c�iv�� ������a��i�y F��s F �F� 1997� a�� Taji�a�s D<br />
�Taji�a 1989� a�� �is�a�ch �is��i���i��s �R�����s<br />
& Ha�p����i�� 1992� �� i�f��� ���c���� �������aphic<br />
his���y �f p�p���a�i��s a�� c��a���s. D���ai��s ��<br />
�a����ia��s a�� ����h��s a��� p����ish��� i� Pa���s��<br />
����sch & Haas�� �2006�.<br />
F�� D. discolor Pa���s�� ����sch & Haas�� �2006�<br />
show little molecular variance within populations<br />
a�� ����i��s�� ��� �is�i�c� �������ic s���c�����<br />
����w����� va�i��s �����ai� �a����s ac��ss E���p��.<br />
Most populations are significantly differentiated<br />
�as��� �� F ST a�� ���ac� ���s�s �f p�p���a�i��<br />
differentiation, and most haplotypes are private<br />
�� a si������ �����ai� �a����. Phy����������ic a�a��ys��s<br />
���v��a�� �����p �iv�������c�� ����w����� ������aphica����y<br />
is���a���� ��i���a���s. C���i������ �h��s�� ���s����s s�����s�<br />
�ha� pas� f�a������a�i�� is �h�� p���i����� p��c��ss<br />
s���c���i�� �h�� p�p���a�i��s ac��ss E���p��. T��s�s<br />
�f s������c�iv�� ������a��i�y a�� �is�a�ch �is��i���i��s<br />
s�����s���� ���c���� �������aphic ���pa�si�� �f �h�s��<br />
p�p���a�i��s wi�h hap����yp�� �v�����ap. Th�� hi�h<br />
level of genetic differentiation between mountain<br />
�a����s a�� ��s�i�a���s �f �������aphic his���y<br />
p��vi��� ��vi����c�� �ha� a� ����as� ������v��� i����p��������<br />
refugia existed over different lengths of time<br />
�v��� �h�� P����is��c�����. I� pa��ic���a� ���f��ia a���<br />
hyp��h��sis��� i� �h�� ����h-w��s����� �a����s �� �h��<br />
I����ia� P���i�s���a; i� �h�� vici�i�y �f �h�� Py��������s;<br />
�h�� �assif C�����a��; �h�� s���h-w��s����� ���ps; �h��<br />
����i�� ����hw��s� �f �h�� ���ps ���a� �h�� J��a a��<br />
V�s���s �����ai�s a�� �h�� B��ac� F����s�; i� �h��<br />
c�����a�� G����a� hi�h��a��s; i� �h�� �a����s s���h-<br />
��as� �f �h�� ���ps; i� �h�� ������y �����ai�s; i� �h��<br />
vici�i�y �f �h�� Ta��a �a����s; i� �h�� Ca�pa�hia�s; a��<br />
�h�� �a����s �� �h�� s���h���� Ba���a� P���i�s���a. �a�y<br />
�f �h��s�� ����i��s hav�� ������ c��si������� i�p���a��<br />
refugial centres for other species as well (e.g. Hewitt<br />
2004a�� �; Pa���s 2004�. ���s��� �a�y �f �h��s�� ����i��s<br />
are hypothesised areas of diversification based on<br />
the large number of caddisfly and other endemic<br />
sp��ci��s �cc���i�� h����� �Pa���s 2004�� �a��ic�y 2006�.<br />
H�w��v����� s���� �f �h��s�� a���as�� i� pa��ic���a� �h��<br />
����h���� ����i��s�� a��� �f pa��ic���a� i�������s� a��<br />
hav�� ��� ������ c��si������� as ���f��ia�� c�������s i�<br />
�h�� pas�. This is ����� f�� �h�� ����i�� ����hw��s� �f<br />
�h�� ���ps a�� �h�� c�����a�� G����a� hi�h��a��s. Th��<br />
��iq��� a�� �������ic �������ic ��i���a���s f���� i�<br />
�h��s�� ����i��s a�� ��vi����c�� f�� s��c���a�y c���ac�<br />
i� �h�� E�������i���� �f p���vi��s��y s��pa�a���� ��i���a���s<br />
81
S. Pauls, T. Lumbsch, P. Haase Glacial refugia of the montane caddisfly Drusus discolor (Rambur, 1842)<br />
82<br />
s�������y s�����s�s �ha� �h����� w����� ���acia�� ���f��ia<br />
i� �h��s�� ����i��s i� which p�p���a�i��s �f D.<br />
discolor s��viv��� si�c�� w������ ���f���� �h�� ��as� ���acia��<br />
�a�i��� �Pa���s�� ����sch & Haas�� 2006�.<br />
I����p�������� �f �i���c� ���ca�i���� �a��ic�y �1983��<br />
1988� p��p�s��s �ha� i� �h�� vici�i�y �f ���aci���s �h�����<br />
��s� hav�� ������ p���cipi�a�i�� a�� �h�s a��s� s����<br />
s����a�s�� which c����� hav�� s���v��� as ���f��ia. H��<br />
�h�����f���� s�����s�s ���acia�� ���f��ia i� �����ai�s<br />
�� hi����s i� �h�� vici�i�y �f ���aci���s. ��s� �f �h��<br />
���f��ia s�����s���� f�� D. discolor fit this pattern.<br />
����� �f �h��� a��� ���ca���� ���a� �����ai� ����i��s��<br />
which w����� ���acia����. G��acia�i��s a��� ���w� f���<br />
hi�h ������va�i��s �f �h�� Ca��a��ia� �����ai�s�� �h��<br />
Py��������s�� �assif C�����a���� ���ps�� V�s���s ��s.�� J��a<br />
��s.�� B��ac� F����s��� �h�� Ca�pa�hia� �a����s a�� �h��<br />
����h���� Rh���pi ��s. �H����ha�s �H����ha�s & �i�����h �i�����h<br />
1939; P�����sch 1997�. Th�� Th�� c�����a�� c�����a�� G����a� G����a� hi�h��a��s hi�h��a��s<br />
w����� a���� ����� �� ����ss c���s�� �� �h�� ����h���� ���acia��<br />
f�i����; s���� ����i��s w����� v���y c���s�� ���.�. Ha���<br />
��s.�. ����h���h s����a� ����si�y �ay hav�� ������<br />
��ch ���w��� ���i�� ��i��� P����is��c����� ���acia�i��<br />
p���i��s�� wa���� was p���s��a���y a��ways ����i��<br />
s����wh����� i� �h�� p���i���acia�� ����i�� �Thi������a��<br />
19�0; �a��ic�y 1983�. ���s��� f�ssi�� ����ai�s f���<br />
aq�a�ic C������p����a f���� �h����h��� �h�� ��as�<br />
140��000 y��a�s f��� �h�� G�a�� Pi���� p��a� ��� i� �h��<br />
V�s���s ��s. �P������ 1994��� s�����s� �ha� s�i�a�����<br />
c���i�i��s f�� ����i��-wa���� sp��ci��s �cc������<br />
�h����h��� �h�� c���� p���i��s �~ 140��000 �� ~ 30��000<br />
y��a�s a��� i� �h�� hi�h��a��s ����w����� �h�� ����h����<br />
a�� s���h���� i���a�� ic�� sh�����s.<br />
In general, caddisfly species are known to adapt<br />
�h��i� ��if�� cyc���� �� wa���� ����p���a����� ���i��<br />
different development stages (e.g. Enders &<br />
Wa����� 1996; Fisch��� 2003�. ����� �h�� D��si�a����<br />
v���y s���w�� ��� s�cc��ssf��� ���� ���v�����p����� has<br />
��v��� ������ ��s���v��� a� ����p���a�����s ����w�����<br />
2°C and 3.5°C in Drusus rectus rectus �D�ca�ps &<br />
P�j��� 197���� whi���� D. annulatus sh�w��� p��as�ici�y<br />
i� a����� w��i�h� a�� ���y si���� ���p�������� a�����<br />
a ��a�i���� �f wa���� ����p���a����� �Wa����� 200��.<br />
Chaetopteryx villosa a��s� sh�ws p��as�ici�y i� a�����<br />
si���� a�� w��i�h� a����� a ����p���a����� ��a�i����<br />
�Wa����� 200�� a�� �h�� ��if�� cyc���� was p����������<br />
�� a �w�-y��a� cyc���� i� c������� c��i�a���s �������s���<br />
& Tyss�� 1984�. C. villosa c��p�������� i�s ��if�� cyc����<br />
successfully at 2°C water temperature (Wagner<br />
1986, 1990) and even close to 0°C water temperature<br />
�Wa������� p���s��a�� c�����ica�i���. �s D. discolor<br />
is a sp��ci��s which is ��� ���s��ic���� ���� ��� capa�����<br />
�f s��vivi�� i� ������������y c���� wa���� ha�i�a�s ���.�.<br />
�ava��i��� 1992��� i�s p���sis����c�� w����� p���s��a���y<br />
��� hav�� ������ ��i�i���� �y ���w ����p���a�����s�� ��� �y<br />
occurrence of permanently, turbulently flowing<br />
wa���� ���i��s�� wh����� i� w����� hav�� f���� s�i�a�����<br />
and su���ciently oxygenated habitats. Constantly<br />
����i�� wa���� �v��� ha�� s��s��a���s w����� hav��<br />
presumably been su���cient habitats for D. discolor<br />
�� s��viv�� i�s ��a�va�� s�a���.<br />
Only little is known about the adult phase and<br />
���havi��� �f D. discolor. W�� �h�����f���� ca����<br />
imply specific habitat requirements of the species<br />
f�� s�cc��ssf��� c����ship�� �a�i�� a�� �vip�si�i��.<br />
H�w��v����� ��a�va�� a�� a�����s �f �h�� sp��ci��s �cc��<br />
i� ha�i�a�s w������ a��v�� �h�� ������ ��i��� i� ���h �h��<br />
���ps a�� �h�� s���h���� E���p��a� �����ai� �a����s<br />
��a��ic�y 1988�� �ava��i��� 1992�� Pa���s 2004�. I� a��s�<br />
occurs in the floodplains of large Alpine rivers,<br />
��i��� �h�� Isa� �H���i�� 199���� which a��� �a���a����y<br />
f����� �f ������ v������a�i��. I� �h�s s�����s p��a�si�����<br />
�ha� �h�� sp��ci��s was a����� �� s��viv�� i� a �����a<br />
or steppe like environment with little or only low<br />
�ipa�ia� v������a�i���� a�� ����s ��� ���q�i��� ������s as<br />
swa��i�� �� c�������a�i�� ��a���a��s �� ha�i�a�.<br />
Conclusions<br />
Th�� s���y �f �i��ch����ia�� p�p���a�i�� s���c�����<br />
i� D. discolor sh�ws �ha� �his aq�a�ic ���a�is�s<br />
reacted differently to Pleistocene cooling than<br />
�a�y �������s��ia�� sp��ci��s. I� p���sis���� i� ��������s<br />
���f��ia �v��� �����ip���� ���acia�� cyc����s�� a�����wi��<br />
�a�y ���ca�� �������ic c��a���s �� f���. ����� �f �h��s��<br />
���f��ia ��i�� i� c�����a�� E���p��. Th�� hyp��h��s��s �as���<br />
�� �h��s�� ���s����s c��p��������� �h����i��s f�������<br />
�ai���y �� �������s��ia�� sp��ci��s�� which c��ai� �ha�<br />
���acia�� ���f��ia w����� ���ca���� ����y i� �h�� s���h����<br />
E���p��a� ����i��s.<br />
Th�� ���w�������� �f p���sis�i�� aq�a�ic i�s��c�s i�<br />
c�����a�� E���p��a� hi�h��a��s �� �h�� ���� ha��<br />
a�� �h�� p��as�ici�y i� ��if�� his���y ��ai�s �f s��v���a��<br />
caddisfly species related to water temperature on<br />
the other hand, suggest that the pattern observed<br />
i� D. discolor �i�h� ��� ��� ��iq����� ��� �ha� ��h���<br />
c����-�������a�� aq�a�ic i�s��c�s �ay a��s� hav��<br />
s��viv��� i� �h��s�� ����i��s. Th�� ��vi����c�� c�������c����<br />
f�� D. discolor is a first molecular indication for<br />
�h�� ���is����c�� �f a ����p �f a�i�a��s�� which ���ac����<br />
si�i��a���y �� P����is��c����� c��i�a��� c����i�� a��<br />
Malicky (1983) defined as elements of the dinodal<br />
�i���� �yp��.<br />
<strong>Ferrantia</strong> • 55 / 2008
S. Pauls, T. Lumbsch, P. Haase Glacial refugia of the montane caddisfly Drusus discolor (Rambur, 1842)<br />
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� C��a�is�ic ��a��ysis �f Ph�����ypic �ss�cia�i��s<br />
Wi�h Hap����yp��s I�f������� F��� R��s��ic�i��<br />
E�����c����as�� �appi�� a�� DN� ���q����c��<br />
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Thi������a�� �. 19�0. - V�������i����s���schich���<br />
���� �üßwass����i���w����� E���pas. Di��<br />
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�f Cha����p����y� vi�����sa �T�ich�p����a�. H���a�c�ic<br />
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Wagner R. 1990. - Influence of temperature,<br />
ph���p���i�� a�� ����i�i�� �� ���w�h<br />
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Wagner R. 2005. - The influence of stream water<br />
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�I�s��c�a�� T�ich�p����a� a����� �h�� B���i�����ach<br />
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<strong>Ferrantia</strong> • 55 / 2008
A. Schmidt-Kloiber et al. The Indicator Database for European Freshwater Invertebrates<br />
The Indicator Database for European Freshwater<br />
Invertebrates<br />
Abstract<br />
�a�y �iv��� ass��ss����� sys����s c���������y ���v�����p��� ��<br />
i�p��������� �h�� E���p��a� Wa���� F�a���w��� Di���c�iv��<br />
a��� �as��� �� �����ics �si�� a����c�����ica�� i�f���a�i��<br />
on macroinvertebrate taxa. The EU funded AQEM and<br />
�T�R p��j��c�s hav�� c��pi����� a ��is� �f aq�a�ic �ac��i�v��������a���<br />
�a�a a�� a� ass�cia���� ��c�����ica�� �a�a�as����<br />
c��p�isi�� i�f���a�i�� ��i��� f�����i�� ���havi�����<br />
p���f������c��s f�� �����i���i�a�� ������s �� sap���ic c���i�i��s<br />
Introduction<br />
Th�� ����p��a�� a�� spa�ia�� �is��i���i��s �f<br />
f���shwa���� ���a�is�s a��� �i�h���y c�����c���� ��<br />
asp��c�s �f ����������aphy p���s �h��i� physi�����ica��<br />
a�� ���havi���a�� ���sp��s��s �� va�yi�� ����v����s �f<br />
���vi��������a�� fac���s. Th�� c��pa�a�iv����y ����<br />
���w�������� �f �h��i� ���vi��������a�� ������s a��<br />
�f ���sp��s��s �� va�i��s ���vi��������a�� fac���s<br />
has ����� �� a f���q����� �s�� as ��i��i��ica���s i�<br />
wa���� �a�a�������� a�� i� app��i��� ��c�����y �s����<br />
R�s�������� & R��sh 1993�� Davis & �i��� 199��.<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Astrid Schmidt-Kloiber<br />
Wolfram Graf<br />
Otto Moog<br />
BOKU - U�iv���si�y �f Na���a�� R��s���c��s & �pp��i��� �if�� �ci���c��s�� Vi����a<br />
D��pa������� �f Wa������ ����sph����� a�� E�vi��������<br />
I�s�i����� �f Hy����i�����y a�� �q�a�ic Ec�sys���� �a�a��������<br />
�a� E�a������ ���a�� 17<br />
�-1180 Vi����a�� ��s��ia<br />
as��i�.sch�i��-����i����@����.ac.a�<br />
http://www.boku.ac.at/hfa<br />
Armin Lorenz<br />
Daniel Hering<br />
U�iv���si�y �f D�is����-Ess���<br />
I�s�i����� �f Bi�����y & G�����aphy<br />
D��pa������� �f Hy����i�����y<br />
U�iv���si�ä�ss��. �<br />
D-4�117 Ess���<br />
�� 9146 E���p��a� �ac��i�v��������a��� sp��ci��s. Th��<br />
�a�a�as�� is ��w f���h��� ����������� wi�hi� �h�� EU f������<br />
p��j��c� E���-��i�pacs�� pa��ic���a���y �y pa�a�������s�� which<br />
�i�h� ��� s���si�iv�� �� �i���c� �� i��i���c� i�pac�s �f c��i�a���<br />
cha���� ���.�. a���i���i�a�� a�� ����p���a����� p���f������c��s ��<br />
��if�� his���y ��ai�s�. F�c�s is a��s� �iv��� �� �h�� ��c�����i��a��<br />
�is��i���i�� �f sp��ci��s acc���i�� �� I����i��s �1978�. Fi�s�<br />
�a�������� i�v��������a��� ����p a��� T�ich�p����a.<br />
Th�� �ai� ��a�� �f �h�� aq�a�ic aq�a�ic �ac��-i�v��������a���<br />
�ac��-i�v��������a���<br />
�a�a��is� a�� i�s ass�cia���� ��c�����ica�� �a�a�as��<br />
p���s������� h����� is �� p��vi��� a ����� f�� �h�� ��c�����ica��<br />
ass��ss����� �f wa���� ���i��s i� c��p��ia�c�� wi�h<br />
�h�� ������s �f �h�� Wa���� F�a���w��� Di���c�iv�� �EC �EC<br />
2000/60; WFD�.<br />
�i�c�� �a�a �� a����c�����y a�� �is��i���i�� a���<br />
scattered about thousands of sources, the database<br />
ai�s a� �a�i�� �his �a�if���� i�f���a�i�� avai��a�����<br />
�� �h�� i�������s���� p����ic i� a� ��asi��y acc��ssi�����<br />
f���.<br />
85
A. Schmidt-Kloiber et al. The Indicator Database for European Freshwater Invertebrates<br />
86<br />
Methods – Development of the<br />
database<br />
Th�� �ac��-i�v��������a��� �a�a��is� p����ish��� ��<br />
http://www.freshwaterecology.info is a �living<br />
document� that was first set up for the purposes<br />
of the EU funded AQEM project (www.aqem.de).<br />
Th�� ai� �f �his p��j��c� was �h�� ���v�����p����� a��<br />
���s�i�� �f a� i������a���� sys���� f�� �h�� ass��ss�����<br />
�f �h�� ��c�����ica�� q�a��i�y �f s����a�s a�� �iv���s<br />
�h����h��� E���p�� �si�� �����hic �ac��-i�v���-<br />
�����a���s. Th�� ��i�h� p��j��c� �������� c�����i��s<br />
���s��ia�� C����ch R��p����ic�� G����a�y�� G�����c���� I�a��y��<br />
Th�� N���h�����a��s�� P�����a���� �w������� ���v�����p���<br />
multi-metric assessment systems for different<br />
s����a� �yp��s�� which a��� app��ica����� �h����h a<br />
computer software (ASTERICS, formerly AQEM<br />
Riv��� �ss��ss����� P����a������ �� ��� ��w����a����<br />
a� www.aq���.����. �s �h�� ass��ss����� sys����s<br />
���q�i��� ��c�����ica�� ���w�������� �f �h�� �a�a i� was<br />
��ss����ia�� �� c�������c� i�f���a�i�� �� ���h �cc��-<br />
����c�� �f �a�a wi�hi� �h�� pa������ c�����i��s�� a��<br />
��c�����ica�� i�f���a�i�� f�� a c��sis����� a�� �����ia�����<br />
�a�a�as��. T� achi��v�� �his ��a�� �h�� �ac��-i�v������brate<br />
taxalist builds on the scientific expertise of<br />
many scientists from different zoological fields, fields,��<br />
��iv���si�i��s�� ���a�isa�i��s a�� s�ci���i��s.<br />
I� �h�� s�cc�����i�� EU f������ �T�R p��j��c�<br />
�www.���-s�a�.a�� �ha� ai���� f�� �h�� s�a��a�disation<br />
of river classifications, the taxa and<br />
a����c�����y �a�a�as�� was ����������� wi�h �a�i��a��<br />
ch��c���is�s f��� D����a���� F�a�c���� G���a� B�i�ai���<br />
�a�via�� P���a�� a�� ����va�ia.<br />
Th�� s���ps �a���� ��wa��s �h�� ���v�����p����� �f �h��<br />
www.f���shwa������c�����y.i�f� �a�a�as�� ������ �h��<br />
above mentioned two projects were:<br />
● Designation of persons responsible for<br />
the national checklists: from each partner<br />
c�����y a� ����as� ���� p���s�� was s������c���� ��<br />
��� ���sp��si����� f�� p��vi�i�� i�f���a�i��<br />
�� �a�i��a�� ���c���s �f �h�� �a��������<br />
i�v��������a��� ����ps �s���� c�����y ch��c���is�s<br />
www.f���shwa������c�����y.i�f��.<br />
● Quality control: species validity, species<br />
������c��a����� a�� sy���y�y w����� ch��c����<br />
�y ac���w��������� a�� app��v��� ���p����s �s����<br />
�a�����ic ���p����s �� www.f���shwa������c�����y.<br />
i�f��.<br />
● Compiling the database: the data were<br />
c���i���� i��� a �� �cc��ss �a�a�as����<br />
�si�� �h�� p��v��� s���c����� �f �h�� ��s��ia�<br />
software ECOPROF that has been<br />
���v�����p��� f�� �a�a s���a��� a�� ��va���a�i��<br />
�www.��c�p��f.a��.<br />
● Compiling the autecological information:<br />
as a �asic �a�a s���c���� ���is�i�� ��c�����ica��<br />
classifications were critically reviewed and<br />
a��p����. I� ������ �f p�i��i�isa�i�� w�� �s���<br />
�1� �h�� Fa��a �q�a�ica ��s��iaca �����<br />
199��� 2002��� �2� �h�� Bava�ia� �is� ��ch�����j��<br />
& C�����i�� 1996� a�� �3� ��h��� �a�i��a�� ��is�s.<br />
If p�ssi������� s������c���� sp��ci��s w����� assi����� ��<br />
���p����s a�� p��j��c� pa������s f�� a���������� �f<br />
their classifications.<br />
● Coding the new autecological information:<br />
���p����i�� �� �h�� pa�a��������� �a�a w����� �iv��� a<br />
������ica�� c���� �si�� ��i�h��� a 10 p�i��s sys����<br />
�� a si������ ca������y assi�������.<br />
Th�� �a�a�as�� is ��w f���h��� i�p��v���<br />
wi�hi� �h�� EU f������ p��j��c� E���-��i�pacs<br />
�www.�������i�pacs.�c��.ac.����� which ���a��s wi�h<br />
�h�� ��va���a�i�� �f c��i�a��� cha���� i�pac�s ��<br />
E���p��a� f���shwa���� ��c�sys����s. Th�� f�c�s<br />
wi�hi� E���-��i�pacs ��i��s �� ��c�����ica�� pa�a�������s<br />
�������va�� f�� ass��ssi�� �h�� i�pac� �f c��i�a���<br />
cha���� �� f���shwa���� ���a�is�s. Th��s�� c�v���<br />
�a�a �� ��c�����i��a�� �is��i���i�� ���.�.�� �a�a i� hi�h<br />
�����ai� a���as �ay ��� pa��ic���a���y s���si�iv�����<br />
��if�� cyc���� pa�a�������s ���.�.�� i�c���as��� wa����<br />
temperature may particularly effect the timing<br />
�f ����������c����� ����p���a����� p���f������c��s a��<br />
c������� p���f������c��s ���.�.�� c������� ���sis�a�c�� �i�h�<br />
��� a� i�p���a�� ass��ss����� f��a������� if �ischa����<br />
patterns will change in future). This information is<br />
c��pi����� f�� s������c���� i�v��������a��� ����ps�� s�a��i��<br />
with <strong>Trichoptera</strong> (caddisflies). Chironomidae<br />
(non-biting midges), Plecoptera (stoneflies) and<br />
Ephemeroptera (mayflies) will follow.<br />
Results<br />
Taxonomical and autecological<br />
information<br />
Th�� f���shwa������c�����y.i�f� �a�a�as�� c���������y<br />
h����s i�f���a�i�� �� a ���a�� �f 9146 E���p��a�<br />
�����hic i�v��������a��� sp��ci��s�� ca������is��� i��� 1411<br />
<strong>Ferrantia</strong> • 55 / 2008
A. Schmidt-Kloiber et al. The Indicator Database for European Freshwater Invertebrates<br />
�������a�� 300 fa�i��i��s a�� 33 hi�h��� �a�����ic<br />
����ps ���s���y ������s�. I�c����i�� "w���i�� �a�a"<br />
��i��� sp��ci��s-����ps �h�� ��is� c���ai�s 12191 �a�a.<br />
36 ��c�����ica�� pa�a�������s a�� i��ic��s�� wi�h va�yi��<br />
numbers of classified taxa, are included into the<br />
�a�a�as��. G������a����y�� �h�� si� ��c�����ica�� pa�a�������s��<br />
�� which ��s� i�f���a�i�� is avai��a������� a��� ��y����<br />
����a�� �sap���ic i��ic��s��� s����a� ����a�i��<br />
p���f������c��s ����p��c���� �is��i���i�� �f a sp��ci��s<br />
wi�hi� �h�� �����i���i�a�� ��a�i���� �f a s����a� f���<br />
�h�� s���c�� �� �h�� ����h��� c������� a�� s��s��a���<br />
��ic��ha�i�a�� p���f������c��s�� f��c�i��a�� f�����i�� a��<br />
���c����i�� �yp��s. F�� T�ich�p����a i�f���a�i�� is<br />
a�����a�y a��i�i��a����y avai��a����� ����a��i�� ��c����-<br />
�i��a�� �is��i���i�� �s���� ������w��� �������is� a��<br />
ha�i�a� sp��cia��is�s.<br />
�i�c�� ��s� �f �h�� �������va�� i�f���a�i�� i� ��i����ature<br />
is recorded in narrative form, two different<br />
����h��s �10 p�i��s sys������ si������ ca������y<br />
assi������� sys����� w����� �s��� �� ��a�sf��� �h��<br />
��c�����ica�� ���w�������� i��� ������ica�� va�����s. This<br />
numerical information offers the opportunity to<br />
��� p��c��ss��� f�� ��c�����ica�� q�a��i�y ass��ss�����.<br />
� c��p���h���siv�� �v���vi��w �f �h�� �a�a�as���� a<br />
�isc�ssi�� a�� s���� ���a�p����s f�� �h�� �s�� �f<br />
��c�����ica�� pa�a�������s a��� �iv��� �y �ch�i��-<br />
K���i���� ��� a��. �2006�.<br />
Ecoregional distribution<br />
Th�� ��c�����i�� c��c��p� �f I����i��s �1978� was<br />
a��p���� �y �h�� WFD as �as�� f�� �yp�����y a�� �h��<br />
���v�����p����� �f ass��ss����� ����h�������i��s �a�����<br />
11�. Th�����f������ �h�� c��pi��a�i�� �f �h�� ��c�����i��a��<br />
i�f���a�i�� �� �a�a wi�hi� �h�� f���shwa������c�����y.<br />
i�f� �a�a�as�� is ���� �f �h�� �aj�� ��a��s �f E���-<br />
��i�pacs. This i�f���a�i�� is ��w avai��a����� f��<br />
T�ich�p����a. Th�� �a�a�as�� ca� ��� q����i��� f��<br />
different ecoregions and the results can either be<br />
�isp��ay��� as �a�����s �� as �is��i���i�� �aps. �s a�<br />
���a�p���� Fi����� 1 ������s��a���s �h�� ��c�����i��a��<br />
�is��i���i�� �f Plectrocnemia kisbelai B���sa���a����<br />
1967 i� �h�� ���ps a�� i� �h�� Ca�pa�hia�s.<br />
Discussion and outlook<br />
� s���� ������s�a��i�� �f �����hic i�v��������a���<br />
��c�����y is a p������q�isi��� f�� �h�� i�p���������a�i��<br />
�f �i�����ica�� app��ach��s �� E���p��a� aq�a�ic<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Fig.1: Ecoregional distribution of Plectrocnemia kisbelai<br />
Botosaneanu, 1967 in the Alps and in the Carpathians;<br />
source of map (modified): European Environment Agency<br />
(www.eea.eu.int)<br />
��c�sys���� �a�a��������. Th�� Th�� ���v�����p����� ���v�����p����� �f �f<br />
ass��ss����� sys����s f�� �h�� ��c�����ica�� s�a��s �f<br />
f���shwa����s has ��������s��y i�c���as��� i� ���c����<br />
y��a�s�� p�i�a�i��y �� ������ �h�� ���q�i��������s �f �h��<br />
WFD. Ra��i�� f��� ��a�i�i��a�� sap���ic wa����<br />
q�a��i�y ���i���i�� �� �h�� ��va���a�i�� �f va�i��s<br />
s����ss��s a�� �h��i� i�pac� �� �����hic i�v��������a���s��<br />
�h��s�� ass��ss����� ����h�������i��s hav�� ���c����<br />
����� a�� ����� c��p����� a�� s�phis�ica����.<br />
Th�� �ai� p��p�s�� �f �h�� aq�a�ic aq�a�ic �ac���ac��i�v��������a��� �a�a��is� a�� i�s ass�cia���� ��c�����ica��<br />
�a�a�as�� is �� �� p��vi��� p��vi��� a �asic �asic ����� ����� f�� f�� �h�� �h��<br />
��c�����ica�� ass��ss����� �f wa���� ���i��s �ha�<br />
should be available for the scientific public at a<br />
c��pa�a�iv����y ��a���y s�a��� �f i�s ���v�����p�����.<br />
Th�����f������ �h�� sp��ci��s i�v������i��s a�� �h��<br />
ecological rankings are in different stages of<br />
c��p����������ss f�� ��s� �f �h�� �a�������� c�����i��s<br />
a�� �a�����ic ����ps. C��s��q�������y�� �h�� �a�a<br />
i�v������y ����s ��� ���c��ssa�i��y ���p���s���� �h�� s�a���<br />
of the art of a country�s recorded species: these<br />
��is�s hav�� �� ��� ������s���� as a� �p���a�i��a�� �����<br />
f�� �i�-���i���i�� p��j��c�s ������ �h�� a�spic��s<br />
�f �h�� Wa���� F�a���w��� Di���c�iv��. N��v����h������ss��<br />
besides its operational character, the final product<br />
sh����� ���p���s���� a ������ica����y ��a�sf�������� s�a���<br />
87
A. Schmidt-Kloiber et al. The Indicator Database for European Freshwater Invertebrates<br />
88<br />
�f �h�� a�� �a�a�as�� �f E���p��a� ����������aphic a��<br />
��c�����ica�� ���w�������� �� �����hic i�v��������a���s.<br />
Th�� f������ ai�s �f �h�� �a�a�as�� ���v�����p����� a���<br />
defined as:<br />
● Completion of national benthic invertebrate<br />
�a�a i�v������i��s �ch��c���is�s� f�� a���� E���p��a�<br />
countries and adjustment with the findings of<br />
�h�� Fa��a E���pa��a ����p �www.fa��a����.<br />
����.<br />
● Filling the gaps in our knowledge of the<br />
��c�����ica�� pa�a�������s ����a���� s� fa�.<br />
● Inclusion of additional ecological parameters<br />
s�ch as ����p���a����� p���f������c���� ���sis�a�c��<br />
�� �����h�s�� hy�������ica�� p���f������c����<br />
���p����c�iv�� cyc����s a�� ��if�� cyc���� ���a�i����<br />
a���i����� p���f������c���� a�� ��h���s. � sp��cia�� f�c�s<br />
wi���� ��� �� w�����a��-������wa����-i�����ac�i��s<br />
wi�h �h�� �iv��� c���i��� as a� ����i�y �f aq�a�ic<br />
sys����s i� �h�� s���s�� �f ��a����a�� a�� v����ica��<br />
c�����c�ivi�y.<br />
Whi���� �h�� ���v�����p����� �f ass��ss����� sys����s<br />
c���� �� �h�� f������ �h�� p���f���a�c�� �f a����c�����ica��<br />
studies, which often form the base of these<br />
sys����s�� s�����s �� ��� ���c���asi�� ���� �� �h�� fashi��<br />
f�� "�p-��-�a���" sci���c��s. Th�� �ap ����w����� ���<br />
�asic ���w�������� �f i��ica���s a�� �h�� �������<br />
of different so-called indicator-based assessment<br />
sys����s is�� i� fac��� ���c��i�� ����a������ which<br />
s�����s �� ��� c����a�ic���y. F���a�����a�� a��<br />
app��i��� sci���c��s ������ �� ���v�����p sy�ch�����s��y.<br />
Therefore, it is important to fill as many as possible<br />
�f �h�� �a�����ic a�� a����c�����ica�� �aps wi�hi�<br />
�h�� f���shwa������c�����y.i�f� �a�a�as��. Th�� �����<br />
ecologically classified species are included into<br />
a� ass��ss����� ����h�������y�� �h�� ����� ��i�����y �h��<br />
������� wi���� ���c���� ���h q�a��i�a�iv����y p�w���f���<br />
a�� i�c���asi����y s���si�iv�� �� �h�� f����� �a���� �f<br />
possible environmental influences. Effective<br />
ass��ss����� p����a����s �� ��va���a��� �h�� ��c�����ica��<br />
s�a��s �f f���shwa���� sys����s ca� c����i����� �� �h��<br />
�v���a���� h��a���h �f �h�� aq�a�ic ���vi��������.<br />
Acknowledgements<br />
W�� ����a���y app���cia��� �h�� w��� �f a���� �h�� �a�����ic<br />
���p����s wh� v�������������� f�� �h�� �a�����ic<br />
va��i�i�y ch��c�i�� �s���� s���� �a�����ic �a�����ic ���p����s ���p����s �� ��<br />
www.f���shwa������c�����y.i�f��. �. W�� W�� a��s� a��s� wa�� wa�� �� ��<br />
�ha�� R������ V���� f�� c��p����� ���ch�ica�� s�pp���<br />
a�� ���a��isa�i��. Tha��s �� �i��� F��s�� f�� �h��<br />
co-ordination of the STAR project (Contract No:<br />
EVK1-CT 2001-00089��� �� �a��i� K����a� f�� c�-<br />
���i�a�i�� �f �h�� E���-��i�pacs p��j��c� �C����ac�<br />
No: GOCE-CT-2003-505540) and to all partners<br />
i� �h��s�� p��j��c�s f�� �h��i� c����i���i�� �� �h��<br />
�a�a�as��.<br />
References<br />
Davis W. �. & �i��� T. P. ����s� 199�. - Bi�����ica��<br />
ass��ss����� a�� c�i����ia. T����s f�� wa����<br />
���s���c�� p��a��i�� a�� ���cisi�� �a�i��. ���wis<br />
P���ss�� B�ca Ra����� F����i�a.<br />
E���p��a� C���issi�� 2000. - Di���c�iv�� 2000/60/<br />
EC. Es�a���ishi�� a f�a���w��� f�� c�����i�y<br />
action in the field of water policy. E���p��a� European<br />
C���issi�� PE-CON� 3639/1/100 R��v 1��<br />
����������.<br />
I����i��s J. ����� 1978. - �i���fa��a E���pa��a. G�s�av G�s�av<br />
Fischer Verlag, Stuttgart.<br />
Moog O. (ed) 1995. - Fauna Aquatica Austriaca – A<br />
C��p���h���siv�� �p��ci��s I�v������y �f ��s��ia�<br />
�q�a�ic O��a�is�s wi�h Ec�����ica�� N����s.<br />
��s��ia� F������a�� �i�is��y f�� ���ic�������� a��<br />
Forestry, Wasserwirtschaftskataster, Vienna:<br />
����s��-����af �i�����.<br />
���� O. ����� 2002. - Fa��a �q�a�ica ��s��iaca<br />
– A Comprehensive Species Inventory of<br />
��s��ia� �q�a�ic O��a�is�s wi�h Ec�����ica��<br />
N����s. 2 �� ���i�i��. ��s��ia� F������a�� �i�is��y<br />
f�� ���ic���������� F����s��y�� E�vi�������� a��<br />
Water Management, Wasserwirtschaftskataster<br />
Vienna: loose-leaf binder.<br />
R�s�������� D. �. & R��sh V. H. ����s� 1993. - F���shwa����<br />
�i����i���i�� a�� �����hic �ac��i�v������-<br />
��a���s. Chap�a� & Ha������ N��w Y����� ������.<br />
�ch�����j�� U. & C�����i�� �. 1996. - ������isch��<br />
Typisi������ ���� aq�a�isch��� �a���fa��a.<br />
I�f���a�i��s����ich��� ���s Bay���isch��� �a����samtes<br />
für Wasserwirtschaft 4/96.<br />
�ch�i��-K���i���� �.�� G�af W.�� �������� �. & ����<br />
O. 2006. - The AQEM/STAR taxalist - a pan-<br />
E���p��a� �ac��-i�v��������a��� ��c�����ica��<br />
�a�a�as�� a�� �a�a i�v������y. Hy����i�����ia<br />
Hy����i�����ia<br />
566: 325-342.<br />
<strong>Ferrantia</strong> • 55 / 2008
I. Schrankel et al. Checklist of the <strong>Trichoptera</strong> of the Grand Duchy of Luxembourg<br />
Checklist of the <strong>Trichoptera</strong> of the Grand Duchy<br />
of Luxembourg - First revision<br />
A first checklist of the <strong>Trichoptera</strong> of Luxembourg<br />
was p����ish��� i� 2002 ��ch�a������ ��� a��. 2002�<br />
i�c����i�� 178 sp��ci��s.<br />
D��� �� ���w i�v��s�i�a�i��s 7 sp��ci��s ca� ��� a�����.<br />
Wormaldia occipitalis �Pic������ 1834� a�� Wormaldia<br />
mediana McLachlan, 1878 of the first list are replaced<br />
�y Wormaldia occipitalis �yp�� 1 a�� Wormaldia<br />
occipitalis �yp�� 2. Wormaldia mediana �c�ach��a���<br />
1878 is ���p��c���� �� �cc�� i� ����������� ����� ���<br />
�� a�����s c����� ��� f���� y���.<br />
Glossosoma boltoni C���is�� 1834 was w������y<br />
identified and turned out to be Glossosoma conformis<br />
N����iss�� 1963 a�� Ceraclea alboguttata Ha������ 1860<br />
is ��w a sy���y� �f Ceraclea albimacula �Ra������<br />
1877� ��a��ic�y 200��.<br />
Systematical and nomenclatorical changes after<br />
R������ �2004� hav�� ������ �a���� i��� c��si����a�i��.<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Isabel Schrankel<br />
R�������i���� 14<br />
�-7661 ��������ach<br />
isa�����.sch�a������@��ai��.c��<br />
Peter Neu<br />
H��i��i������������ 1<br />
D-�4317 Kas����<br />
p������.����@��ich�p����a-�p.���<br />
Alain Dohet<br />
C������� ��� R��ch���ch�� P����ic - Ga��i���� �ipp�a��<br />
41 ���� �� B�i����<br />
�-4422 B����va��<br />
��h���@��ipp�a��.���<br />
Fernand Schoos<br />
B�iw������w���� �<br />
�-7418 B�sch���f<br />
f����a��.sch��s@sic��a.���<br />
Th�s�� �h�� ac��a��is��� ch��c���is� i�c������s 183<br />
sp��ci��s.<br />
Bold = N��w sp��ci��s i� c��pa�is�� wi�h �h�� ��is� �f<br />
�ch�a������ ��� a��. �2002� �2002�<br />
* = Systematic or nomenclatural changes after<br />
R������ �2004�<br />
Rhyacophilidae Stephens, 1836<br />
1 * Rhyacophila dorsalis dorsalis (Curtis,<br />
1834)<br />
2 Rhyacophila fasciata Ha������ 18�9<br />
3 Rhyacophila laevis Pic������ 1834<br />
4 Rhyacophila obliterata �c�ach��a��� 1863<br />
� Rhyacophila philopotamoides �c�ach��a��� 1879<br />
6 Rhyacophila praemorsa �c�ach��a��� 1879<br />
7 Rhyacophila pubescens Pic������ 1834<br />
8 Rhyacophila tristis Pic������ 1834<br />
89
I. Schrankel et al. Checklist of the <strong>Trichoptera</strong> of the Grand Duchy of Luxembourg<br />
90<br />
Glossosomatidae Wallengren, 1891<br />
9 Glossosoma conformis N����iss�� 1963<br />
10 Synagapetus iridipennis �c�ach��a��� 1879<br />
11 Agapetus delicatulus �c�ach��a��� 1884<br />
12 Agapetus fuscipes C���is�� 1834<br />
13 Agapetus cf. laniger �Pic������ 1834�<br />
14 Agapetus ochripes C���is�� 1834<br />
Hydroptilidae Stephens, 1836<br />
1� Ptilocolepus granulatus �Pic������ 1834�<br />
16 Agraylea multipunctata C���is�� 1834<br />
17 Agraylea sexmaculata C���is�� 1834<br />
18 Allotrichia pallicornis �Ea����� 1873�<br />
19 Hydroptila angulata ��s����y�� 1922<br />
20 Hydroptila forcipata �Ea����� 1873�<br />
21 Hydroptila simulans ��s����y�� 1920<br />
22 Hydroptila sparsa C���is�� 1834<br />
23 Hydroptila vectis C���is�� 1834<br />
24 Oxyethira flavicornis �Pic������ 1834�<br />
2� Tricholeiochiton fagesii �G�i�a���� 1879�<br />
26 Orthotrichia costalis �C���is�� 1834�<br />
27 Ithytrichia lamellaris Ea����� 1873<br />
Philopotamidae Stephens, 1829<br />
28 Philopotamus ludificatus �c�ach��a��� 1878<br />
29 Philopotamus montanus �D���va��� 1813�<br />
30 Philopotamus variegatus ��c�p���i�� 1763�<br />
31 Wormaldia occipitalis type1<br />
32 Wormaldia occipitalis type2<br />
33 Wormaldia subnigra �c�ach��a��� 186�<br />
34 Chimarra marginata ��i��a���s�� 1767�<br />
Psychomyiidae Curtis, 1835<br />
3� Psychomyia pusilla �Fa��ici�s�� 1781�<br />
36 Tinodes assimilis �c�ach��a��� 186�<br />
37 Tinodes dives �Pic������ 1834�<br />
38 Tinodes pallidulus �c�ach��a��� 1878<br />
39 Tinodes rostocki �c�ach��a��� 1878<br />
40 Tinodes unicolor �Pic������ 1834�<br />
41 Tinodes waeneri ��i��a���s�� 17�8�<br />
42 Lype phaeopa �����ph���s�� 1836�<br />
43 Lype reducta �Ha������ 1868�<br />
Ecnomidae Ulmer, 1903<br />
44 Ecnomus tenellus �Ra������ 1842�<br />
Polycentropodidae Ulmer, 1903<br />
4� Cyrnus crenaticornis �K������a�i�� 18�9�<br />
46 Cyrnus flavidus �c�ach��a��� 1864<br />
47 Cyrnus insolutus �c�ach��a��� 1878<br />
48 Cyrnus trimaculatus �C���is�� 1834�<br />
49 Holocentropus dubius �Ra������ 1842�<br />
�0 Holocentropus picicornis �����ph���s�� 1836�<br />
�1 Neureclipsis bimaculata ��i��a���s�� 17�8�<br />
�2 Plectrocnemia brevis �c�ach��a��� 1871<br />
�3 Plectrocnemia conspersa �C���is�� 1834�<br />
�4 Plectrocnemia geniculata �c�ach��a��� 1871<br />
�� Polycentropus flavomaculatus �Pic������ 1834�<br />
�6 Polycentropus irroratus C���is�� 183�<br />
Hydropsychidae Curtis, 1835<br />
�7 Cheumatopsyche lepida �Pic������ 1834�<br />
�8 Hydropsyche angustipennis �C���is�� 1834�<br />
�9 Hydropsyche botosaneanui �a�i���vic-<br />
G�sp������ic�� 1966<br />
60 Hydropsyche bulgaromanorum Malicky,<br />
1977<br />
61 Hydropsyche contubernalis �c�ach��a��� 186�<br />
62 Hydropsyche dinarica �a�i���vic�� 1979<br />
63 Hydropsyche exocellata D�f����� 1841<br />
64 Hydropsyche fulvipes �C���is�� 1834�<br />
6� Hydropsyche incognita Pi�sch�� 1993<br />
66 Hydropsyche instabilis �C���is�� 1834�<br />
67 Hydropsyche modesta Navas, 1925<br />
68 Hydropsyche pellucidula �C���is�� 1834�<br />
69 Hydropsyche saxonica �c�ach��a��� 1884<br />
70 Hydropsyche silfvenii U�������� 1906<br />
71 Hydropsyche siltalai Döh������� 1963<br />
72 Diplectrona felix �c�ach��a��� 1878<br />
Phryganeidae Leach, 1815<br />
73 Trichostegia minor �C���is�� 1834�<br />
74 Agrypnia pagetana C���is�� 183�<br />
7� Agrypnia varia �Fa��ici�s�� 1793�<br />
76 Oligotricha striata ��i��a���s�� 17�8�<br />
77 Phryganea bipunctata R�����i�s�� 1783<br />
78 Hagenella clathrata �K������a�i�� 1848�<br />
Brachycentridae Ulmer, 1903<br />
79 Brachycentrus maculatus �F���c��y�� 178��<br />
80 Brachycentrus montanus K��apa������� 1892<br />
81 Brachycentrus subnubilus C���is�� 1834<br />
82 Micrasema longulum �c�ach��a��� 1876<br />
83 Micrasema minimum �c�ach��a��� 1876<br />
84 Micrasema setiferum �Pic������ 1834�<br />
<strong>Ferrantia</strong> • 55 / 2008
I. Schrankel et al. Checklist of the <strong>Trichoptera</strong> of the Grand Duchy of Luxembourg<br />
Lepidostomatidae Ulmer, 1903<br />
8� Lepidostoma hirtum �Fa��ici�s�� 177��<br />
86 Lasiocephala basalis �K������a�i�� 1848�<br />
87 Crunoecia irrorata �C���is�� 1834�<br />
Limnephilidae Kolenati, 1848<br />
Dicosmoecinae Schmid, 1955<br />
88 Ironoquia dubia �����ph���s�� 1837�<br />
Drusinae Banks, 1916<br />
89 Anomalopterygella chauviniana �����i��� 1874�<br />
90 Drusus annulatus �����ph���s�� 1837�<br />
91 Ecclisopteryx dalecarlica K������a�i�� 1848<br />
Limnephilinae Kolenati, 1848<br />
Limnephilini Kolenati, 1848<br />
92 Anabolia nervosa �C���is�� 1834�<br />
93 Glyphotaelius pellucidus �R�����i�s�� 1783�<br />
94 Grammotaulius nigropunctatus �R�����i�s�� 1783�<br />
9� Grammotaulius submaculatus �Ra������ 1842�<br />
96 Limnephilus affinis C���is�� 1834<br />
97 Limnephilus auricula C���is�� 1834<br />
98 Limnephilus binotatus C���is�� 1834<br />
99 Limnephilus bipunctatus C���is�� 1834<br />
100 Limnephilus centralis C���is�� 1834<br />
101 Limnephilus decipiens �K������a�i�� 1848�<br />
102 Limnephilus extricatus �c�ach��a��� 186�<br />
103 Limnephilus flavicornis �Fa��ici�s�� 1787�<br />
104 Limnephilus fuscicornis Ra������ 1842<br />
10� Limnephilus griseus ��i��a���s�� 17�8�<br />
106 Limnephilus hirsutus �Pic������ 1834�<br />
107 Limnephilus ignavus �c�ach��a��� 186�<br />
108 Limnephilus italicus McLachlan, 1884<br />
109 Limnephilus lunatus C���is�� 1834<br />
110 Limnephilus marmoratus C���is�� 1834<br />
111 Limnephilus rhombicus ��i��a���s�� 17�8�<br />
112 Limnephilus sparsus C���is�� 1834<br />
113 Limnephilus stigma C���is�� 1834<br />
114 Limnephilus vittatus �Fa��ici�s�� 1798�<br />
11� Phacopteryx brevipennis (Curtis, 1834)<br />
Stenophylacini Schmidt, 1955<br />
116 Allogamus auricollis �Pic������ 1834�<br />
117 Enoicyla pusilla �B�����is������ 1839�<br />
118 Halesus digitatus ��ch�a���� 1781�<br />
119 Halesus radiatus �C���is�� 1834�<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
120 Halesus tessellatus �Ra������ 1842�<br />
121 Hydatophylax infumatus ��c�ach��a��� 186��<br />
122 Melampophylax mucoreus �Ha������ 1861�<br />
123 Micropterna lateralis �����ph���s�� 1837�<br />
124 Micropterna nycterobia �c�ach��a��� 187�<br />
12� Micropterna sequax �c�ach��a��� 187�<br />
126 Micropterna testacea �G�����i��� 1790�<br />
127 Parachiona picicornis �Pic������ 1834�<br />
128 *Potamophylax cingulatus cingulatus<br />
(Stephens, 1837)<br />
129 Potamophylax latipennis �C���is�� 1834�<br />
130 Potamophylax luctuosus �Pi������� &<br />
Mitterpacher, 1783)<br />
131 Potamophylax nigricornis �Pic������ 1834�<br />
132 Potamophylax rotundipennis �B�a������ 18�7�<br />
133 Stenophylax mitis �c�ach��a��� 187�<br />
134 Stenophylax mucronatus McLachlan, 1880<br />
13� Stenophylax permistus �c�ach��a��� 189�<br />
136 Stenophylax vibex �C���is�� 1834�<br />
Chaetopterygini Hagen, 1858<br />
137 Annitella obscurata ��c�ach��a��� 1876�<br />
138 Chaetopteryx major �c�ach��a��� 1876<br />
139 Chaetopteryx villosa �Fa��ici�s�� 1798�<br />
Apataniidae Wallengren, 1886<br />
140 Apatania fimbriata �Pic������ 1834�<br />
Goeridae Ulmer, 1903<br />
141 Goera pilosa �Fa��ici�s�� 177��<br />
142 Lithax niger �Ha������ 18�9�<br />
143 Lithax obscurus �Ha������ 18�9�<br />
144 Silo nigricornis �Pic������ 1834�<br />
14� Silo pallipes �Fa��ici�s�� 1781�<br />
146 Silo piceus B�a������ 18�7<br />
Leptoceridae Leach, 1815<br />
147 Athripsodes albifrons ��i��a���s�� 17�8�<br />
148 Athripsodes aterrimus �����ph���s�� 1836�<br />
149 Athripsodes bilineatus ��i��a���s�� 17�8�<br />
1�0 Athripsodes cinereus �C���is�� 1834�<br />
1�1 Athripsodes commutatus �R�s��c��� 1874�<br />
1�2 Athripsodes leucophaeus �Ra������ 1842�<br />
1�3 Ceraclea albimacula �Ra������ 1877�<br />
1�4 Ceraclea annulicornis �����ph���s�� 1836�<br />
1�� Ceraclea dissimilis �����ph���s�� 1836�<br />
1�6 Ceraclea fulva (Rambur, 1842)<br />
1�7 Ceraclea nigronervosa �R�����i�s�� 1783�<br />
91
I. Schrankel et al. Checklist of the <strong>Trichoptera</strong> of the Grand Duchy of Luxembourg<br />
92<br />
1�8 Ceraclea senilis �B�����is������ 1839�<br />
1�9 Leptocerus interruptus �Fa��ici�s�� 177��<br />
160 Leptocerus tineiformis C���is�� 1834<br />
161 Adicella filicornis �Pic������ 1834�<br />
162 Adicella reducta ��c�ach��a��� 186��<br />
163 Triaenodes bicolor �C���is�� 1834�<br />
164 Oecetis furva �Ra������ 1842�<br />
16� Oecetis lacustris �Pic������ 1834�<br />
166 Oecetis notata �Ra������ 1842�<br />
167 Oecetis ochracea �C���is�� 182��<br />
168 Oecetis testacea �C���is�� 1834�<br />
169 Setodes argentipunctellus McLachlan, 1877<br />
170 Setodes punctatus �Fa��ici�s�� 1793�<br />
171 *Mystacides azureus (Linnaeus, 1761)<br />
172 Mystacides longicornis ��i��a���s�� 17�8�<br />
173 *Mystacides niger (Linnaeus, 1758)<br />
Molannidae Wallengren, 1891<br />
174 Molanna angustata C���is�� 1834<br />
Odontoceridae Wallengren, 1891<br />
17� Odontocerum albicorne ��c�p���i�� 1763�<br />
Sericostomatidae Stephens, 1836<br />
176 Notidobia ciliaris ��i��a���s�� 1761�<br />
177 Oecismus monedula �Ha������ 18�9�<br />
178 Sericostoma schneideri Kolenati, 1848<br />
179 Sericostoma personatum ��p���c�� i� Ki��y<br />
& �p���c���� 1826�<br />
Beraeidae Wallengren, 1891<br />
180 Beraea maura �C���is�� 1834�<br />
181 Beraea pullata �C���is�� 1834�<br />
182 Beraeodes minutus ��i��a���s�� 1761�<br />
183 Ernodes articularis �Pic������ 1834�<br />
References<br />
�a��ic�y H. 200�. - Ei� ��������i������s V�������ich�is<br />
der Köcherfliegen (<strong>Trichoptera</strong>) Europas und<br />
���s ����i�����a�����i�����s. �i������ �i�����isch��<br />
Beiträge 37/1: 533-596.<br />
R������ B. 2004. - �ys����a�isch��s V�������ich�is ����<br />
Köcherfliegen (<strong>Trichoptera</strong>) Deutschlands -<br />
Fortschreibung 02/2004. Entomologie heute 16:<br />
93-107.<br />
�ch�a������ I.�� N��� P.J.�� D�h��� �. & �ch��s F. 2002.<br />
- Die Köcherfliegen-Fauna im Großherzogtum<br />
Luxemburg. Lauterbornia 43: 47-64.<br />
<strong>Ferrantia</strong> • 55 / 2008
F. Sipahiler Zoogeographical characteristics of the <strong>Trichoptera</strong> Fauna of Turkey<br />
Zoogeographical characteristics of the <strong>Trichoptera</strong><br />
Fauna of Turkey<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Füsun Sipahiler<br />
Hacettepe Üniversitesi<br />
E�i�i� Fa�ü�����si<br />
F��� Bi��i������i Bö��ü�ü<br />
TR-06800 B��y���p���� ���a�a<br />
fusunsip@hacettepe.edu.tr<br />
Keywords: Turkey, Anatolia, Camili, Macahel, <strong>Trichoptera</strong>, faunistics, distribution, centre of<br />
endemism, isolation, new record, zoogeography.<br />
Abstract<br />
Z��������aphica�� a�a��ysis �f �h�� T�ich�p����a fa��a �f<br />
T�����y i� �w� ������aphica�� ����i��s�� i� ����h��as����� a��<br />
northwestern Anatolia and some distribution patterns are<br />
presented. The Caddisfly fauna of Turkey is represented<br />
�y 402 �a�a�� �389 sp��ci��s a�� 13 s��sp��ci��s� ��������i�� ��<br />
80 �������a i� 22 fa�i��i��s. Th�� ���i�a�c�� �f �h�� E���p��a�<br />
sp��ci��s is �h�� cha�ac����is�ic f��a����� �f �h�� fa��a �42 %�;<br />
91 sp��ci��s a��� wi�����y �is��i������ i� E���p�� �22.6 %��� 62<br />
sp��ci��s �1�.�%� sh�w s���h��as����� ����i�����a���a� �yp�� �f<br />
�is��i���i��; 1� sp��ci��s �is��i����� h���a�c�ic �� pa����a�c�ic.<br />
O��� �f �h�� i�p���a�� cha�ac����is�ics �f �h�� fa��a�� is �h��<br />
���i�a�c�� �f Ca�casia� fa��a i� ����h��as����� T�����y.<br />
1� % �f �h�� sp��ci��s a��� f���� i� �h�� Ca�cas�s. �i�������<br />
�f �h�� ���w� 402 sp��ci��s/s��sp��ci��s a��� f���� ����y i�<br />
T�����y a�� I�a�. 6 % �f �h�� sp��ci��s wi�h a wi���sp���a�<br />
�is��i���i�� �Pa����a�c�ic �� H���a�c�ic� 3� % �f �h�� ���w�<br />
sp��ci��s a��� �������ic�� which is �h�� hi�h��s� �a��� �f<br />
�������is� wi�hi� �h�� ����i�����a���a� c�����i��s.<br />
Introduction<br />
Th�� s���i��s �� �h�� T�ich�p����a fa��a �f T�����y<br />
hav�� ������ i� �h�� 19. C������y. I� �h�� �y��psis �f<br />
T�ich�p����a �f �h�� E���p��a� Fa��a�� 6� sp��ci��s a���<br />
ci���� f��� �sia �i��� ��c�ach��a��� 1874-1880�.<br />
Th�� sp��ci��s ���sc�i���� �y �c�ach��a� f��� T�����y<br />
w����� f��w�� ����ai�i�� a��s� �h�� �������ics ���ay;<br />
�h��s�� a��� Tinodes manni �c�ach��a��� Limnephilus<br />
ponticus �c�ach��a� a�� Sericostoma mesopotamicum<br />
�c�ach��a�. I� a��i�i���� Drusus concolor K���p�y��<br />
1908�� ���sc�i���� �� �h�� ����i��i�� �f �h�� 20. C������y<br />
from Keşiş Dagh (Uludağ) (Malicky, 1988: 1) is an<br />
E�c����i�� �h�� �������ics�� which a��� f���� i� ����h��as�����<br />
T�����y�� a����s� a���� �h�� �����a�iv��s �f �h�� �������ic sp��ci��s<br />
a��� a��s� E���p��a�. Ev��� i� ����h��as����� ��a����ia 20 %<br />
�f �h�� �������ics hav�� �h��i� c���s�� �����a�iv��s i� E���p��.<br />
Th�� T�ich�p����a fa��a �f ����h��as����� T�����y is �����a����<br />
�� Ca�casia�/T�a�sca�casia� fa��a; 60 sp��ci��s �1� %�<br />
�is��i����� i� �h�� Ca�cas�s �� �h����h I�a�; 44 sp��ci��s<br />
�10.9 %� �f which a��� f���� ����y i� T�����y a�� �h��<br />
Ca�cas�s.<br />
Th�� si�i��a�i�i��s wi�h �h�� I�a�ia� fa��a a��� ����ss p���i�����;<br />
70 sp��ci��s �17 %� �ha� �cc�� i� T�����y a��� a��s� f���� i�<br />
I�a�; 16 sp��ci��s �is��i����� ����y i� ���h c�����i��s. O���<br />
�f �h�� cha�ac����is�ics �f �h�� T���ish T�ich�p����a fa��a is<br />
�h�� hi�h �a��� �f �h�� �������is�. ��a��ysis �f �h�� �������ics<br />
a�� �h��i� �����a�iv��s i��ica���s �h�� c�������s �f �������is� i�<br />
����h��as����� ��a����ia a�� �h�� fa��a �f �h�� ����i�� is ���<br />
�h�� ��������i�� pa�� �f �h�� Ca�casia� fa��a ��� sh�ws i�s<br />
�w� cha�ac����is�ics. ���v���a�� �yp��s �f �h�� �is��i���i�� �f<br />
Turkish <strong>Trichoptera</strong> are figured and discussed.<br />
�������ic sp��ci��s f���� i� a s�a���� a���a i� �h�� B��sa<br />
province (Malicky & Sipahiler, 1993). After 1970�s,<br />
�h�� ������� �f s���i��s i�c���as���; i� 1978�� 114 sp��ci��s<br />
f�� T�����y w����� ��is���� �B���sa���a�� & �a��ic�y��<br />
1978). In 1984, the first list included 201 species,<br />
was p����ish��� ��a��ic�y & �ipahi������� 1984�. �a������<br />
i� 1987�� �h�� ������� �f �h�� ���w� sp��ci��s ���ach���<br />
�� 23��� i� 1993 �� 291 a�� i� 199� �� 313 ��ipahi����� &<br />
�a��ic�y�� 1987; �a��ic�y & �ipahi������� 1993; �ipahi�������<br />
1996�. I� �h�� ��as� ���ca����� �a�y ���w sp��ci��s a��<br />
���c���s w����� p����ish����� i�c���asi�� �h�� ������� �f<br />
���w� sp��ci��s/s��sp��ci��s �� 386 ��ipahi������� 200��.<br />
I� �h�� p���s���� s���y�� �h�� ��a���s� ���c���s w����� a�������<br />
93
F. Sipahiler Zoogeographical characteristics of the <strong>Trichoptera</strong> Fauna of Turkey<br />
94<br />
s� �ha� �h�� ���w� sp��ci��s �f �h�� fa��a i�c���as��s ��<br />
402 sp��ci��s/s��sp��ci��s ��������i�� �� 80 �������a i�<br />
22 fa�i��i��s. Oecetis notata Ra������ 1842 is a ���w<br />
���c��� f�� �h�� T���ish fa��a�� �isc�v������ ���c������y<br />
i� ����hw��s����� T�����y.<br />
I� �his s���y�� �������a�� �����i���s �f �h�� ����������aphy<br />
�f T���ish T�ich�p����a a�� �h�� fa��is�ic a�a��ysis �f<br />
����h��as����� a�� ����hw��s����� ��a����ia ����i��s<br />
a��� �iv���.<br />
T�����y is a �����ai���s c�����y�� �ivi���� �� 8<br />
������aphica�� ����i��s �Fi�.1�. N���h���� ��a����ia��<br />
ca������� �h�� B��ac� ���a R���i���� is ���������� i� �h�� s���h<br />
wi�h �h�� p��a���s �f �h�� ��as����� a�� c�����a�� ��a����ia<br />
����i��s. P����s �����ai� �a���� �Ka�a����i��<br />
�����ai�s� �������� pa�a��������s �� �h�� c�as� a�� ���c����s<br />
hi�h��� �h����h �h�� ��as�. Kac�a� �����ai�s i�<br />
�h�� Ri���� p��vi�c�� is �h�� hi�h��s� pa�� �3917 �� �f<br />
�h�� �����ai� �a����. Th��s�� �����ai�s a��� �h��<br />
�������si��s �f �h�� Ca�cas�s ��� a��� s��pa�a���� f���<br />
�h��s�� �����ai�s �y Ri��i-K��a va������y i� G�����ia.<br />
This s��pa�a�i�� is a��s� ��vi����� i� �h�� c��p�si�i��<br />
�f �h�� T�ich�p����a fa��a �f ����h��as����� ��a����ia;<br />
�h�� ����i�� has i�s �w� �������ics a�� �h�� Ca�casia�<br />
i�vasi��s a��� ����� �� ����ss ��i�i����. O� �h�� ��h���<br />
ha���� s���� �������a ��i��� Cerasma a�� Martynomyia��<br />
which were described first from the Caucasus, have<br />
����� sp��ci��s i� �h�� ����i��.<br />
Va������ys�� ��������i�� v����ica����y a����� �h�� c�as���<br />
s��pa�a��� �h�� P����s �����ai� �a����s. I� �h��<br />
w��s����� pa�� �f �h�� ����i���� �h�� �����ai�s a���<br />
����ss hi�h a�� �h�� va������ys a��� s�����i���s v���y<br />
��a���� ��i��� a p��ai�. I� �h�� ��as� �f �h�� ����i���� �w�<br />
va������ys s��pa�a��� �h�� �����ai�s f��� ��ach ��h���.<br />
O��� �f �h��� is �h�� ���h va������y�� s��pa�a���s �h��<br />
hi�h��s� pa�� �f �h�� �����ai�s �����p��y �� Kaç�a�<br />
a�� Ka�cha�� �����ai�s. This s��pa�a�i�� ca�s���<br />
a ��������ica�� is���a�i�� �f �h�� ����h������s� c������<br />
�f T�����y�� Ca�i��i ��acah����� ����i���� i��ica�i��<br />
c����a���y a c������� �f �������is�.<br />
The zoogeographical outlines<br />
of the <strong>Trichoptera</strong> fauna<br />
The caddisfly fauna of Turkey is represented by 402<br />
�a�a �389 sp��ci��s a�� 13 s��sp��ci��s��� ��������i�� �� 80<br />
�������a i� 22 fa�i��i��s. Th�� fa�i��y ����a��i�a�� is ���<br />
���p���s������� i� T�����y. Th�� �ich���ss �f �h�� sp��ci��s is<br />
s����� ��sp��cia����y i� s���h���� T�����y �168 sp��ci��s� a��<br />
����h��as����� T�����y �140 sp��ci��s�. ����h��as�����<br />
T�����y has ����y 14 sp��ci��s�� c�����sp���i�� �� �h��<br />
a�i� c��i�a��� �f �h�� ����i�� �Ta����� 1�<br />
Fig. 1: Geogrophical regions of Turkey. I, Marmara Region; II, West Anatolia Region; III, North west Anatolia Region;<br />
IV, Central Anatolia Region; V, Mediterranean Region; VI, North east Anatolia Region; VII, East Anatolia Region; VIII,<br />
South east Anatolia Region. Arabic numbers indicate the known species/endemics from each region.<br />
<strong>Ferrantia</strong> • 55 / 2008
F. Sipahiler Zoogeographical characteristics of the <strong>Trichoptera</strong> Fauna of Turkey<br />
Table 1: The list of the families and the number of the known genera/species of <strong>Trichoptera</strong> in Turkey.<br />
E: Endemics, I-VIII: The geographical regions in Turkey, I: Marmara region, II West Anatolia<br />
region, III, North western Anatolia region, IV, Central Anatolia region, VI, North eastern Anatolia<br />
region, VII, East Anatolia region, VIII, South Anatolia region.<br />
Family/ species &<br />
subspecies (total) E Genus Regions/species<br />
I II III IV V VI VII VIII<br />
Rhyac�phi��i�a��/21 7 2 2 4 8 2 � 1� � -<br />
G���ss�s��a�i�a��/19 12 3 4 6 4 4 7 4 8 -<br />
P�i���c�����pi�a��/2 - 1 1 1 2 - 2 2 - -<br />
Hy���p�i��i�a��/�7 18 8 4 27 14 19 27 � 10 2<br />
Phi���p��a�i�a��/12 4 2 4 3 4 1 3 8 - -<br />
P���yc������p��i�a��/21 7 � 10 17 8 8 20 12 7 1<br />
Ec���i�a��/3 1 1 - 1 - 2 2 - 1 2<br />
Psych��yii�a��/31 12 3 6 11 8 4 1� 7 2 -<br />
Hy���psychi�a��/�7 22 3 11 16 16 1� 29 22 26 4<br />
Ph�ya���i�a��/6 1 2 - 1 3 1 3 2 2 -<br />
B�achyc�����i�a��/4 2 2 1 1 2 1 2 2 - -<br />
U����i�a��/2 - 1 - - 1 - - 2 - -<br />
G����i�a��/� - 3 1 - 2 - 1 1 2 -<br />
���pi��s���a�i�a��/10 � 4 2 3 3 2 2 � 2 -<br />
�pa�a�ii�a��/3 2 2 - 1 - - 1 2 1 -<br />
�i����phi��i�a��/76 22 16 18 18 32 19 29 29 31 2<br />
����ic�s���a�i�a��/14 9 � - 6 3 2 2 6 2 -<br />
O�����c���i�a��/1 - 1 - 1 - - - 1 - -<br />
H����ic�psychi�a��/1 - 1 1 - 1 - - - - -<br />
Ca��a��c���a�i�a��/1 - 1 1 1 1 1 1 - - 1<br />
B���a��i�a��/14 9 4 - � � 3 4 4 1 -<br />
���p��c���i�a��/44 9 9 � 21 13 17 14 11 19 2<br />
T��a�� 22/402 80 71 145 128 101 168 140 119 14<br />
E�����ic sp��ci��s/�������a 141 2 � 27 28 14 49 3� 19 2<br />
Endemics % 35 07 18.5 21.8 13.8 29 25 16 14<br />
The significant characteristic of the Turkish<br />
T�ich�p����a fa��a is �h�� hi�h p���c����a��� �f �h��<br />
�������is�. Tw� ��i����phi��i� �������a�� �Rizeiella<br />
a�� Hadimina� a�� 141 �f �h�� ���w� sp��ci��s a���<br />
endemic to Turkey (35 %). Compared to different<br />
c�����i��s �f E���p���� ��.�. i� �h�� p���i�s���a� I�a��y<br />
�h�� p���c����a��� �f �������ics is 29 %�� which is �h��<br />
hi�h��s� �a��� i� �h�� s���h���� ����i��s; i� Basi��ica�a<br />
31 %�� i� Ca��a��ia 32 %�� ��v��� �ici��y sh�ws 32 %<br />
�f �������is�. �i�i��a���y�� �h�� �a��� i� �h�� Ba���a�s is<br />
22 %, in the Iberian Peninsula 13 % (Cianficconi<br />
a� a���� 1997�. E�c����i�� �h�� ����i�����a���a� is��a��s<br />
a�� s���h���� I�a��y�� �h�� Ca�cas�s is �h�� ����y ����i��<br />
wi�h 31 % �f �������ics �ha� c���s�� �� �h�� �a��� �f �h��<br />
T���ish fa��a. Wi�hi� �h�� fa�i��i��s �pa�a�i�a��<br />
�66%��� ����ic�s���a�i�a�� a�� B���a��i�a�� sh�w �h��<br />
hi�h��s� �a��� �f �������is� �64%�.<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Th�� �������ics�� �cc���i�� i� �h�� �a��a�a ����i����<br />
i�c����i�� �h�� E���p��a� pa�� �f T�����y a��� ����y<br />
five species, which are found in the Asian part<br />
�f T�����y. Th�� s���h���� ��a����ia is �h�� �ich��s�<br />
����i���� havi�� 168 sp��ci��s; which �f �h��s�� 49<br />
sp��ci��s a��� �������ics.<br />
Th�� T�ich�p����a fa��a �f T�����y is s�������y �����a����<br />
�� �h�� E���p��a� fa��a �Fi�. 2�. 168 �f �h�� ���w�<br />
402 sp��ci��s �42 %� a��� f���� i� E���p���� �f which<br />
91 sp��ci��s �22.6 %� hav�� E���p��a� �is��i���i����<br />
62 sp��ci��s �1�.�� % �is��i������ i� �h�� s���h��as�<br />
����i�����a���a� ����i�� a�� 1� sp��ci��s sh�w h���a��ic<br />
�� pa����a�c�ic �is��i���i��. Th�� T�ich�p����a fa��a<br />
�f ����h��as����� T�����y is �����a���� �� Ca�casia�/<br />
T�a�sca�casia� fa��a; 60 sp��ci��s �1� %� �is��i����� i�<br />
�h�� Ca�cas�s �� �h����h I�a�. 44 sp��ci��s �10.9 %� �f<br />
which a��� f���� ����y I� T�����y a�� �h�� Ca�cas�s;<br />
95
F. Sipahiler Zoogeographical characteristics of the <strong>Trichoptera</strong> Fauna of Turkey<br />
96<br />
Fig. 2: Similarities of the <strong>Trichoptera</strong> fauna of Turkey to the adjacent regions. The numbers in the brackets indicate<br />
the species that occur only in both regions.<br />
Fig. 3: Distribution of the species of the family Rhyacophilidae in Turkey. Spotted areas indicate the areas of the<br />
listed species.<br />
<strong>Ferrantia</strong> • 55 / 2008
F. Sipahiler Zoogeographical characteristics of the <strong>Trichoptera</strong> Fauna of Turkey<br />
Table 2: The families and the number of the species in different countries (TR: (Sipahiler, 2004, 2005,<br />
2005a and unpublished data), GR: Greece, GB: Grand Britania (Barnard, 1985), A: Austria<br />
(Malicky, 1999), I: Italy (Cianficconi, 2002; Malicky, 2002), BG: Bulgaria (Kumanski, 1985,<br />
1988), RL: Libanon, IL: Israël (B���sa���a�� 1992�, SY: Syria (Sipahiler & Malicky, 1987; Malicky,<br />
1997), IR: Iran (Mirmoayedi &Malicky, 2002; Mey, 2004).<br />
Families TR GR GB A I BG RL IL SY IR<br />
Hy����i�si�a�� - - - - - - - - - 1<br />
Rhyac�phi��i�a�� 21 21 4 24 37 18 2 1 - 4<br />
G���ss�s��a�i�a�� 19 16 6 13 12 14 3 2 1 3<br />
P�i���c�����pi�a�� 2 - - 1 1 - - - - 1<br />
Hy���p�i��i�a�� �7 42 31 27 �0 28 14 1� 4 2�<br />
Phi���p��a�i�a�� 12 12 � 9 22 11 1 1 - 4<br />
P���yc������p��i�a�� 21 16 13 17 30 10 1 2 - 7<br />
Ec���i�a�� 3 1 1 1 1 1 - 2 - 3<br />
Psych��yii�a�� 3 34 12 27 27 12 7 6 1 8<br />
Hy���psychi�a�� �7 29 11 17 24 19 4 4 6 27<br />
Ph�y�a���i�a�� 6 2 10 9 8 4 1 - - 1<br />
B�achyc�����i�a�� 4 3 1 7 6 4 - - 1 2<br />
U����i�a�� 2 1 - - 1 1 - - - -<br />
G����i�a�� � � 3 6 9 6 - - - 1<br />
���pi��s���a�i�a�� 10 4 3 4 4 3 - - - 4<br />
�pa�a�ii�a�� 3 3 1 2 2 - - 1 - -<br />
�i����phi��i�a�� 76 �7 �8 10� 112 73 12 7 6 16<br />
����c�s���a�i�a�� 14 9 2 4 10 2 1 - - 1<br />
O�����c���i�a�� 1 2 1 1 1 1 - - - -<br />
����a��i�a�� - - 2 3 - - - - - -<br />
H����ic�psychi�a�� 1 2 - - 2 1 - - - -<br />
Ca��a��c���a�i�a�� 1 1 - - - 1 - - - -<br />
B���a��i�a�� 14 11 - 7 20 � 1 1 - 1<br />
���p��c���i�a�� 44 34 31 33 33 31 4 7 1 13<br />
Total 402 305 199 317 412 245 51 49 20 120<br />
a���� �h����� 2 sp��ci��s�� Glossosoma capitatum a��<br />
Hydropsyche cornuta a��� a��s� f���� i� ����a��� a��<br />
�y�ia ���sp��c�iv����y.<br />
E�c����i�� �h�� �������ics�� which a��� f���� i�<br />
����h��as����� T�����y�� a����s� a���� �h�� �����a�iv��s �f<br />
�h�� �������ic sp��ci��s a��� a��s� E���p��a�. Ev��� i�<br />
����h��as����� ��a����ia 20 % �f �h�� �������ics hav��<br />
�h��i� c���s�� �����a�iv��s i� E���p��.<br />
T�����y has a �ich fa��a�� c��pa���� �� s����<br />
c�����i��s i� E���p�� a�� i� �h�� �i������ Eas� �Ta����� 2�.<br />
Th�� fa�i��i��s Hy���p�i��i�a�� a�� Hy���psychi�a��<br />
����h wi�h �7 �a�a��� ���p��c���i�a�� �wi�h 44 �a�a�<br />
a�� ����ic�s���a�i�a�� wi�h �14 �a�a� a��� ���s�<br />
���p���s������� i� T�����y i� havi�� hi�h��s� �������<br />
�f �h�� sp��ci��s wh��� c��pa���� �� �h�� E���p��a� a��<br />
�i������ Eas� C�����i��s. Th�� fa�i��y Rhyac�phi��i�a��<br />
is w������ ���p���s������� i� T�����y ��s� �f �h�� sp��ci��s<br />
a��� f���� i� ����h���� ��a����ia �Fi�.3�.<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
�i����phi��i�a�� is �h�� ��a����s� fa�i��y�� ���p���s������� i�<br />
T�����y �y 76 sp��ci��s ��������i�� �� 22 �������a.<br />
Th�� �����s Limnephilus is w������ ���p���s������� wi�h 26<br />
sp��ci��s�� c��pa���� �� s��v���a�� pa��s �f E���p���� ��.�.<br />
i� �h�� Ba���a�s 20 sp��ci��s�� i� I�a��y�� 2� sp��ci��s a�� i�<br />
the Caucasus 21 species are known (Cianficconi,<br />
2002; �a��ic�y�� 1983�.<br />
Th�� si�i��a�i�i��s wi�h �h�� I�a�ia� fa��a a���<br />
����ss p���i�����; 70 sp��ci��s �17%� �ha� �cc�� i�<br />
T�����y a��� a��s� f���� i� I�a�; 16 sp��ci��s a���<br />
�is��i������ ����y i� ���h C�����i��s�� which ��������<br />
�� �h�� fa�i��i��s Hy���p�i��i�a���� Hy���psychi�a����<br />
P���yc������p��i�a���� ���pi��s���a�i�a�� a��<br />
���p��c���i�a��.<br />
Th�� si�i��a�i�i��s wi�h �h�� ���va��i��� fa��a a���<br />
��i�i���� wi�h 34 sp��ci��s; �h�� sp��ci��s �is��i������<br />
����y i� T�����y a�� ���va�� a��� ��� �a�����y�� Hydroptila<br />
97
F. Sipahiler Zoogeographical characteristics of the <strong>Trichoptera</strong> Fauna of Turkey<br />
98<br />
atargatis �a��ic�y�� H. mendli levanti B���sa���a����<br />
Orthotrichia ammanensis �a��ic�y�� Hydropsyche<br />
jordanensis Tj������ a�� Ernodes saltans �a��y��v.<br />
<strong>Trichoptera</strong> fauna of<br />
northeastern Turkey<br />
I� �his ����i�� 140 sp��ci��s/s��sp��ci��s ��������i��<br />
�� �h�� 47 �������a i� 19 fa�i��i��s �cc���� ���c����i��<br />
�h�� fa�i��i��s Ec���i�a���� H����ic�psychi�a�� a��<br />
Ca��a��c���a�i�a��. ��s� �f �h�� sp��ci��s �f �h�� fa�i��y<br />
Rhyac�phi��i�a�� i� T�����y�� �a�����y 1� �f 21 ���w�<br />
�a�a a��� f���� i� �his ����i��.<br />
F��� s�a���� �������a �ha� hav�� ���� �� a f��w<br />
sp��ci��s�� �a�����y�� Philocrena �Rhyac�phi��i�a�����<br />
Kelgena ��i����phi��i�a���� Cha����p����y�i�i���<br />
Martynomyia ����pi��s���a�i�a��� a�� Cerasma<br />
�����ic�s���a�i�a��� a��� �������ic f�� ����h��as�����<br />
��a����ia a�� �h�� Ca�cas�s. ����� �h���<br />
Martynomyia has �w� �f �h�� ���w� �h�����<br />
sp��ci��s a�� Cerasma �h�� ���w� �w� sp��ci��s i�<br />
����h��as����� T�����y. Philocrena trialetica�� �h�� ����y<br />
sp��ci��s �f �h�� �����s Philocrena�� ���p���s������� i� �h��<br />
Ca�cas�s a�� ����h��as����� T�����y. I� a��i�i����<br />
�h�� �������a Apataniana ��pa�a�i�a��� a�� Metaneoa<br />
Fig. 4: Distributions of the genus Ptilocolepus species in Turkey.<br />
��i����phi��i�a���� D��si�a��� a��� ���p���s������� i�<br />
�his ����i�� �y ���� sp��ci��s ��ach. Apataniana borcka<br />
�ipahi����� is �h�� P����is��c����� �����ic��� �isc�v������ i�<br />
Ka�cha�� �����ai�s a� 2200 � a���i����� i� ��a���<br />
a�����. Th�� �����a�iv�� sp��ci��s is Apataniana bulbosa<br />
�a��y��v�� f���� i� c�����a�� �sia. O� �h�� c����a�y��<br />
�h�� �����s Metanoea ���p���s������� i� ����h��as�����<br />
T�����y �y ���� sp��ci��s�� �y M. anatolica �ipahi�������<br />
�h�� �����a�iv��s a��� f���� i� �h�� ���ps a�� W��s�����<br />
E���p�� ��ipahi������� 1999�. Rizeiella �ipahi�����<br />
�Cha����p����y�i�i� is �h�� �������ic �����s�� ���sc�i����<br />
f��� �his ����i���� ���p���s������� �y �w� sp��ci��s.<br />
Th�� fa�i��y P�i���c�����pi�a���� which was �isc�v������<br />
���c������y i� Thai��a�� a�� sh�ws a �����ic� �is��i���i��<br />
wi�h a f��w sp��ci��s f���� i� �h�� ����i�����a���a�<br />
����i�� ��a��ic�y & Cha��a�a�a��������� 1996���<br />
���p���s������� i� T�����y �y 2 sp��ci��s�� Ptilocolepus<br />
colchicus �a��y��v a�� P. dilatatus �a��y��v. B��h<br />
sp��ci��s a��� f���� sy�pa��ica����y i� s��v���a�� p��ac��s<br />
i� ����h��as����� ��a����ia �Fi�.4�.<br />
Th�� a�a��ysis �f �h�� �������ic sp��ci��s a�� �h��i� c���s��<br />
�����a�iv��s �Ta�. 3� i��ica���s �ha� �h�� fa��a �f �h��<br />
����i�� is ��� �h�� ��������i�� pa�� �f �h�� Ca�casia�<br />
fa��a�� ��� sh�ws i�s �w� cha�ac����is�ics. I� �h��<br />
����i���� 1 �������ic �����s a�� 3� �������ic sp��ci��s<br />
�cc��; ����y 6 sp��ci��s hav�� �h��i� c���s�� �����a�iv��s i�<br />
�h�� Ca�cas�s. Th�� �����a�i��ships �f 11 �������ics<br />
<strong>Ferrantia</strong> • 55 / 2008
F. Sipahiler Zoogeographical characteristics of the <strong>Trichoptera</strong> Fauna of Turkey<br />
Table 3: Endemic species and their close relatives in northeastern Turkey.<br />
Family/Species<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Distribution<br />
in Turkey<br />
Close relatives<br />
and their Distributions<br />
Rhyac�phi��i�a��<br />
Rhyacophila arhaviensis �ipahi������� 1986 Ri���� U����w�<br />
R. borcka �ipahi�������1996 ���vi� �Ca�i��i� R. pubescens Pic������ 1834�� E���p��<br />
R. gorgitensis �ipahi������� 1997 ���vi� �Ca�i��i� U����w�<br />
R. zwickorum �a��ic�y�� 1972<br />
G���ss�s��a�i�a��<br />
T�a�������<br />
Ri���������vi��� B����<br />
stigmatica-����p�� E���p��<br />
Synagapetus gorgitensis �ipahi������� 1996<br />
Hy���p�i��i�a��<br />
���vi��Ca�i��i� �����w�<br />
Stactobia cermikensis �ipahi������� 1998 ���vi� �Ca�i��i� S. olgae �a��y��v�� 1927�� T�����s�a�<br />
S. klapaleki �ch�i��� 19�9�� Pa�is�a�<br />
S. lekoban �ipahi������� 1998 ���vi� �Ca�i��i� S. wimmeri �a��ic�y�� 1988�� T�a�����<br />
S. wimmeri �a��ic�y�� 1988<br />
Phi���p��a�i�a��<br />
T�a����� S. lekoban �ipahi������� 1998�� ���vi�<br />
Wormaldia dizkiran �ipahi������� 2001 ���vi� �Ca�i��i� W. hemsinensis �ipahi������� 1987�� Ri����<br />
W. hemsinensis �ipahi������� 1987 Ri���� W. dizkiran �ipahi������� 2001�� ���vi�<br />
W. ikizdere �ipahi������� 2000<br />
P���yc������p��i�a��<br />
Rize, Gümüşhane W.triangulifera �c�ach��a���1878 E���p��<br />
Plectrocnemia rizeiensis �ipahi������� 1987 Ri���� P. brevis �c�ach��a��� E���p��<br />
P. kydon �a��ic�y�� 197� s���h Ba���a�s<br />
Polycentropus yuecelcaglari �ipahi������� 1999<br />
Hy���psychi�a��<br />
���vi� �Ca�i��i� P. segregatus ���y�� 1982�� Ca�cas�s<br />
Hydropsyche gemecika �a��ic�y�� �a��ic�y�� 1981 Gi���s�� �����w�<br />
H. kebab �a��ic�y�� 1974 R���i��s I-VI instabilis-����p<br />
H. orduensis �ipahi������� 1987 O����� ���vi� instabilis-����p<br />
H. yukaritepe �ipahi������� 2004<br />
���pi��s���a�i�a��<br />
O��� instabilis-����p<br />
Martynomyia ayderensis �ipahi������� 1989 Ri������ ���vi� M. tripartita �a��y��v�� 1913�� Ca�cas�s<br />
M. martynovi �ipahi������� 199�<br />
�pa�a�ii�a��<br />
Ri���� �����w�<br />
Apataniana borcka �ipahi������� 1996 ���vi� �Ca�i��i� A. bulbosa �a��y��v�� 1918 �i����ia<br />
�i����phi��i�a��<br />
Drusus bayburti Ca�i��� 1983 R���i��s III�� V��VI��<br />
VII<br />
D. caucasicus U�������� 1907 Ca�cas�s��<br />
R���i�� VII<br />
D. fuesunae �a��ic�y�� 1986 T�a����� D. bayburti Ca�i��� 1983<br />
D. rizeiensis �ipahi������� 1986 Ri���� D. biguttatus Pic������ 1834 E���p��<br />
Limnephilus ponticus �c�ach��a��� 1898 R���i��s II-VI�� Ri���� lunatus-����p�� E���p���� I�a�<br />
Metanoea anatolica �ipahi������� 1986 Ri���� �����w�<br />
Micropterna<br />
�a��ic�y�� 1997<br />
sipahilerae K��a�s�i & Gi���s�� �����w�<br />
Kelgena macahelensis �ipahi������� 1999 ���vi� �Ca�i��i� K. kelensis �a��y��v�� 1926 Ca�cas�s<br />
Rizeiella anatolica �ipahi������� 1986 Ri���� R. camiliensis �ipahi������� 1999 ���vi�<br />
R. camiliensis �ipahi������� 1999 ���vi� �Ca�i��i� R. anatolica �ipahi������� 1986 Ri����<br />
99
F. Sipahiler Zoogeographical characteristics of the <strong>Trichoptera</strong> Fauna of Turkey<br />
100<br />
Family/Species<br />
�31 %� a��� �����w�; 8 �f �h�� �������ics hav�� �h��i�<br />
c���s�� �����a�iv��s ����s��wh����� i� T�����y�� ��� ��s���y i�<br />
�h�� ����i�� a�� 7 �f �h�� sp��ci��s i� E���p���� ��v��� 1<br />
sp��ci��s has a c���s�� �����a�iv�� i� �i����ia.<br />
The centres of endemics of the region<br />
����h���h i� ����h��as����� ��a����ia ��v���y p��vi�c��<br />
has i�s �w� �������ics�� �w� ����i��s�� �a�����y Kac�a�<br />
�����ai�s i� �h�� Ri���� p��vi�c�� wi�h 40 % �f<br />
�������ics a�� Ka�cha�� �����ai�s i� �h�� ���vi�<br />
p��vi�c�� �Ca�i��i ����i��� a��� i�p���a�� c�������s �f<br />
�������is� �s���� Ta�. 3�.<br />
Camili (Macahel) Region in the<br />
Karchal Mountains<br />
Th�� ����h������s� c������ �f �h�� ����i�� sh�ws<br />
i�������s�i�� f��a�����s �f �h�� c��p�si�i�� �f �h��<br />
fa��a�� i��ica�i�� �ha� �his s�a���� a���a ����ai����<br />
is���a���� �������� �ha� �h�� ��h��� pa�� �f ����h��as�����<br />
��a����ia R���i��. ���� �h�� �is��i���i�� �f �h��<br />
�������ics i� �h�� ����h ��as����� T�����y p�i�� a<br />
c������� �f �������ics�� Ka�cha�� �����ai�s �vi����a���<br />
Ca�i��i� i� �h�� ���vi� p��vi�c���� s��pa�a���� �y<br />
���h va������y f��� �h�� Ri���� p��vi�c���� a�� �y Ri��-<br />
K��a ���p���ssi�� f��� �h�� Ca�cas�s�� ���ca���� ���a�<br />
�h�� s�a��� ������� �� G�����ia. Th�� ����i�� is c�v������<br />
wi�h ����s�� s�����pica�� �ai�y f����s�; ��s� �f �h��<br />
places are without human effect, which provides<br />
to the animal species rich and different biotopes.<br />
This s�a���� ����i�� is a� i�p���a�� ���f���� a���a i�<br />
�h�� ���vi� p��vi�c���� has a �ich fa��a wi�h �w�<br />
Distribution<br />
in Turkey<br />
Close relatives<br />
and their Distributions<br />
����ic�s���a�i�a��<br />
Cerasma chairon �a��ic�y�� 1986 Ri���� C. c�����a �c�ach��a��� 1876 Ca�cas�s<br />
Notidobia demelti�� �a��ic�y�� 1974<br />
B���a��i�a��<br />
Ri������ Gü�üsha��� N. forsteri �a��ic�y�� 1974�� Ca�cas�s<br />
Ernodes macahelensis �ipahi������� 1997 ���vi� �Ca�i��i� E. saltans �a��y��v�� 1913 Ca�cas�s�� Ca�cas�s��<br />
I�a��� ���va��<br />
E. rizeiensis �ipahi������� 1987<br />
���p��c���i�a��<br />
Ri���� �����w�<br />
Adicella thalia �a��ic�y�� 1976 T�a����� A. balcanica B���sa���a�� & N�va���<br />
196��� Ba���a�s<br />
Setodes dehensuerae Ca�i� & �a��ic�y�� 1983 ���a��ya�� ���vi��� S. kuehbandneri �a��ic�y�� 1987 Eas�<br />
E�������<br />
��a����ia<br />
�������ics�� �f which �h�� c���s��s� �����a�iv��s a��� f����<br />
i� �h�� ���i�h����i�� Ri���� p��vi�c���� T�a������� i� �h��<br />
Ca�cas�s�� ��v��� i� E���p���� T�����s�a��� Pa�is�a� �� i�<br />
�i����ia �Ta�. 3�. F�� ���a�p������ Ernodes macahelensis<br />
�ipahi����� �B���a��i�a��� is f���� ����y i� Ka�cha��<br />
�����ai�s�� �h�� c���s�� �����a�iv�� sp��ci��s E. saltans<br />
�a��y��v is f���� i� �h�� Ca�cas�s a�� �is��i�����s<br />
i� Ri���� �h����h s���h���� T�����y a�� ���va��<br />
�Fi�.��; si�i��a���y�� Wormaldia dizkiran �ipahi����� is<br />
a� �������ic sp��ci��s �cc���i�� i� Ca�i��i ����i����<br />
whi���� �h�� sis���� sp��ci��s W. hemsinensis �ipahi�����<br />
is f���� i� �h�� Ri���� p��vi�c���� �h�� �is��i���i��s<br />
of the latter and some more species found in this<br />
����i�� w����� �iv��� i� �h�� �Fi�.6�. ����h���h �h��<br />
a���a is ����y 1/6 �f �h�� a���a �f �h�� Ri���� p��vi�c����<br />
�h�� fa�i��y Rhyac�phi��i�a�� ���p���s����s h����� �y<br />
13 sp��ci��s ��������i�� �� �w� �������a�� whi���� i� �h��<br />
���i�h����i�� Ri���� p��vi�c�� has 8 sp��ci��s a�� ����<br />
�����s. I� �h�� ���vi� p��vi�c���� 18 �f �h�� ���w�<br />
3� �������ics �f �h�� ����h ��as����� T�����y ��1 %�<br />
a��� f����; �h�� sp��ci��s�� which a��� �h�� Ca�casia�<br />
�������ics�� �is��i���i�� ����y i� �h�� Ca�cas�s a��<br />
����y i� ����h��as����� ��a����ia�� ���p���s���� h����� �y<br />
18 sp��ci��s. Th�� ������� �f �h�� �������ics ���c���as��s<br />
i� �h�� ���i�h����i�� Ri���� p��vi�c���� �h����� a��� f����<br />
14 �������ics �41 %� a�� 13 Ca�casia� �������ics.<br />
I� a��i�i���� s���� sp��ci��s�� ��i��� Micrasema bifoliatum<br />
�a��y��v �Fi�.7��� Ernodes saltans �a��y��v��<br />
Agapetus caucasicus �a��y��v a�� Limnephilus<br />
ponticus �c�ach��a��� which a��� wi�����y �is��i������<br />
i� T�����y �� i� �h�� s�������i�� a���a�� ��� ���<br />
f���� i� Ca�i��i ����i��. Th��s�� f��a�����s �f �h�� fa��a<br />
i��ica��� is���a�i���� f�� c���i����� ����� p���i��s i�<br />
�h�� pas� ��������ica�� �i���s. I��������� �h�� Ri��i-K��a<br />
���p���ssi�� ����w����� �h�� B��ac� ���a a�� Caspia� ���a<br />
<strong>Ferrantia</strong> • 55 / 2008
F. Sipahiler Zoogeographical characteristics of the <strong>Trichoptera</strong> Fauna of Turkey<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Fig. 5: Distributions of Ernodes saltans Martynov and Ernodes macahelensis Sipahiler (Map<br />
references for the Caucasus Kornouhova, 1986; Levant, Botosaneanu, 1992).<br />
Fig. 6: Distribution of the close related species of <strong>Trichoptera</strong> in northeastern Anatolia and in<br />
the Caucasus (Map reference for the Caucasus Kumanski, 1980).<br />
101
F. Sipahiler Zoogeographical characteristics of the <strong>Trichoptera</strong> Fauna of Turkey<br />
Fig. 7: Distributions of the genus Micrasema species in Turkey and in the Caucasus (Map reference for the Caucasus<br />
Kornouhova, 1986)<br />
102<br />
in the north of the Camili Region was flooded by<br />
�h�� s��a a� �h�� ����i��i�� �f O��i��c������� ����ai�i��<br />
i� �h�� �i������ �i�c�����. I� P��i�c������� �h�� Ri��i-<br />
Kura depression was under the influence of the<br />
Caspia� �asi�; �h�� ��a�s����ssi�� �f �h�� s��a wi�h<br />
��ac�ish wa���� c�v������ �h�� a���a f��� �h�� s���h��as�<br />
(Lüttig & Steffens, 1976). In Pleistocene and even<br />
i� H����c����� �h�� ��v�����i�� �f �h�� P����-Caspia�<br />
�asi� c���i�����; �h�� ��a�s����ssi��s �f �h�� B��ac�<br />
���a was i� �h�� �a�i��� ����v���� i� �h�� i��������acia��<br />
p���i��s�� whi���� �h�� p���via�� ��a�s����ssi��s �f �h��<br />
Caspia� ���a ���� p��ac�� a� �h�� ���� �f i��������acia��<br />
p���i�� a�� ����i��i�� �f ���acia�i��s ����i��a��� &<br />
���i��va�� 199��.<br />
O��� �f �h�� i�������s�i�� f��a�����s �f �h�� Ca�i��i<br />
region is to find some rheophile species that enter<br />
i� �h�� a��pi��� ��a���s f���� �� hi�h �����ai�s.<br />
F�� ���a�p������ i� Nacha����v �a��� ���ca���� a� 29�0<br />
� a���i����� i� �h�� ����i�� �w� Drusus sp��ci��s�� D.<br />
amanus ���y & �ü������� a�� D. rizeiensis �ipahi�����<br />
a��� f����; ���h sp��ci��s a��� a��s� f���� i� Yi���i��<br />
�a��� ���ca���� ���f���� �h�� s���i� �f �h�� Ka�cha��<br />
�����ai�s a� 2800 � a���i�����.<br />
Northwestern Turkey<br />
I� ����hw��s����� T�����y 128 sp��ci��s a��� ���w���<br />
��������i�� �� �1 �������a i� 19 fa�i��i��s. Tw����y-��i�h�<br />
sp��ci��s a��� �h�� �������ics �21.8 %�. Th�� fa�i��i��s<br />
Ec���i�a���� �pa�a�i�a�� a�� O�����c���i�a��<br />
a��� ��� ���p���s������� i� �h�� ����i��. Th�� fa�i��y<br />
H����ic�psychi�a�� �cc��s i� ����hw��s����� pa�� �f<br />
T�����y ��a��a�a a�� ����hw��s����� ��a����ia���<br />
�his ����i�� c����� ��� �h�� ��as����� ��i�i� �f i�s<br />
�is��i���i��. I� �his ����i���� �h����� �ai� �����������s<br />
can be recognized in the fauna:<br />
• E���p��a� �����������s.<br />
Th�� fa��a �f �h�� ����i�� is s�������y �����a����<br />
�� �h�� E���p��a� fa��a�� 81 sp��ci��s �63 %� a���<br />
f���� i� E���p���� �f which 23 sp��ci��s �28 %�<br />
hav�� s���h��as����� ����i�����a���a� �yp�� �f �h��<br />
�is��i���i�� a�� 9 sp��ci��s hav�� pa����a�c�ic ��<br />
h���a�c�ic �is��i���i��.<br />
• Ca�casia� �����������s.<br />
F��������� sp��ci��s �10 %� �is��i����� a��s� i�<br />
�h�� Ca�cas�s a��/�� i� ����h��as����� T�����y��<br />
���pa��i�� �h��i� a���a �h����h �h�� w��s� �Ta�.4�.<br />
<strong>Ferrantia</strong> • 55 / 2008
F. Sipahiler Zoogeographical characteristics of the <strong>Trichoptera</strong> Fauna of Turkey<br />
Table 4: List of the species found in northwestern and northeastern Turkey and/or Caucasicus<br />
Fa�i��i��s<br />
Rhyac�phi��i�a��<br />
Dis��i���i��<br />
1 Rhyacophila clavalis �a��y��v N���h ��as����� T�����y�� Ca�cas�s<br />
2 R. subovata �a��y��v N���h ��as������� s���h���� T�����y�� Ca�cas�s<br />
3 R. zwickorum �a��ic�y<br />
P�i���c�����pi�a��<br />
N���h ��as����� T�����y�� �������ic<br />
4 Ptilocolepus colchicus �a��y��v N���h��as����� T�����y�� s���h���� T�����y�� Ca�cas�s�� I�a�<br />
� P.dilatatus �a��y��v<br />
P���yc������p��i�a��<br />
N���h��as������� s���h���� T�����y�� Ca�cas�s<br />
6 Plectrocnemia latissima �a��y��v<br />
Psych��yii�a��<br />
N���h��as����� T�����y�� ����h���� pa�� �f c�����a�� ��a����ia��<br />
Ca�cas�s�� I�a�<br />
7 Tinodes unidentatus K��apa�����<br />
Hy���psychi�a��<br />
Ca�cas�s<br />
8 Hydropsyche acuta �a��y��v W��s������� ��as������� c�����a�� T�����y�� Ca�cas�s<br />
9 H. lepneva B���sa���a�� N���hw��s������� ��as����� a�� s���h���� T�����y�� Ca�cas�s<br />
10 H. mahrkusha �ch�i� N���h��as����� T�����y�� I�a�<br />
11 H. martynovi B���sa���a��<br />
B�achyc�����i�a��<br />
N���h��as����� T�����y�� Ca�cas�s<br />
12 Micresema bifoliatum �a��y��v<br />
�i����phi��i�a��<br />
N���h��as������� w��s����� a�� s���h���� T�����y�� Ca�cas�s �Fi�. 7�<br />
13 Limnephilus microdentatus �a��y��v<br />
����ic�s���a�i�a��<br />
N���h ��as����� T�����y�� Ca�cas�s<br />
14 Schzopelex grusiense �a��y��v W��s������� ����h��as����� T�����y�� Ca�cas�s<br />
• I�a�ia� �����������s.<br />
Only five species, Hydroptila armathai �ch�i���<br />
Hydropsyche ressli �a��ichy�� Hydropsyche mahrkusha<br />
�ch�i��� Dinarthrum iranicum �ch�i� a��<br />
Polycentropus cf. mazdacus �ch�i� a��� f���� i�<br />
T�����y a�� I�a�.<br />
Th�� sp��ci��s �f �h�� fa�i��y P�i���c�����pi�a�� a��� f����<br />
i� �h�� ����i��; �h�� a���a �f P. dilatatus �a��y��v<br />
���pa��s �h����h �h�� w��s� ��a����ia; ���h sp��ci��s<br />
�cc�� �a�����y i� �h�� s���h �Fi�. 4�.<br />
Th�� fa�i��y �i����phi��i�a�� ���p���s������� i� �h��<br />
����i�� �y 32 sp��ci��s�� which a��� 42 % �f �h�� ���w�<br />
�i����phi��i�s�� ��������i�� �� 10 �������a. Limnephilus<br />
is �h�� ��a����s� �����s wi�h 14 sp��ci��s�� which is<br />
���p���s������� i� ����h��as����� T�����y �y 10 sp��ci��s.<br />
Th�� s�a���� �����s Psilopteryx �Cha����p����y�i�i���<br />
�cc���i�� wi�h � sp��ci��s �a�� � s��sp��ci��s<br />
�f P. psorosa K������a�i� i� c�����a�� E���p���� �h��<br />
Ca�pa�hia�s a�� �h�� Ba���a�s�� ���p���s������� i� �his<br />
����i�� �y ���� sp��ci��s a�� ���� s��sp��ci��s�� which is<br />
�h�� s���h���� ��i�i� �f �h�� �is��i���i�� a���a �f �h�� �����s<br />
�Fi�. 8�. �i�i��a���y�� Limnephilus extricatus �c�ach��a���<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Goera pilosa Fa��ici�s �G����i�a����� Oecetis notata<br />
Ra���� ����p��c���i�a����� �cc���i�� i� ��a���� a���a<br />
i� E���p���� ��ach f���� ����y i� ���� p��ac�� i� �h��<br />
����i���� i��ica�i�� s���h���� a�� ��as����� ��i�i�s �f<br />
�h�� �is��i���i��s i� �his a���a. Rhyacophila tristis<br />
Pic���� has a��s� a ��a���� a���a i� E���p���� f���� i�<br />
�his ����i�� i� s��v���a�� p��ac��s a�� ����s ��� ���pa��<br />
�h����h �h�� ��as� I� �his ����i�� 28 �������ic sp��ci��s<br />
�cc�� �Ta�. ���� 10 �f �h��s�� hav�� c���s�� �����a�iv��s i�<br />
E���p�� �36%�. ���v��� �������ic sp��ci��s hav�� �h��i�<br />
c���s�� �����a�iv��s i� T�����y �2� %� a�� � sp��ci��s i� �h��<br />
Ca�cas�s �18 %�.<br />
Distribution Patterns<br />
I� �h�� ���acia�� p���i��s �f �h�� P����is��c������� ��a����ia<br />
was i� �h�� p���via�� p���i��s �ha� ca�s��� �����<br />
p���cipi�a�i��s�� ���s����i�� i� �h�� �����a��������� �f<br />
�h�� a���as �f �h�� ��a���s a�� �h�� �iv���s i� T�����y<br />
a�� f���a�i�� �f ���w ��a���s i� �h�� s�i�a����� a���as.<br />
I��������� ��sp��cia����y i� c�����a�� ��a����ia �ha� has a�<br />
a�i� c��i�a��� ���ay�� �h����� was a ��a���� ��a��� i� �h��<br />
K��ya p��ai��� �f which �h�� ���p�h was 2� �. I� is<br />
103
F. Sipahiler Zoogeographical characteristics of the <strong>Trichoptera</strong> Fauna of Turkey<br />
104<br />
Fig. 8: Distributions of some species of <strong>Trichoptera</strong>, which are widely distributed in Europe and the distribution<br />
of the genus Psilopteryx in Turkey.<br />
Table 5: Endemic species and their close relatives in northwestern Turkey.<br />
No North western Turkey<br />
Distribution in<br />
Close relatives<br />
endemics<br />
Rhyac�phi��i�a��<br />
Turkey<br />
and their distribution<br />
1 Rhyacophila osellai �a��ic�y ����h���� T�����y R. polonica �c�ach��a��� E���p��<br />
2 R. zwickorum �a��ic�y<br />
G���ss�s��a�i�a��<br />
N���h��as����� T�����y R. stigmatica K������a�i�� E���p��<br />
3 Agapetus karabagi Ça�i� - A. laniger Pic������ E���p��<br />
4 Synagapetus anatolicus Ça�i� W��s� a�� s���h T�����y S. birgi �ipahi������� w��s����� T�����y<br />
� Glossosoma yigilca �ipahi�����<br />
Hy���p�i��i�a��<br />
- G. capitatum �a��y��v�� ����h ��as���<br />
��as��� w��s� T�����y�� Ca�cas�s�� ���va��<br />
6 Hydroptila abantica �ipahi����� - H. ovacikensis �ipahi������� ��as� T�����y<br />
7 H. oemerueneli �ipahi����� - H. brissaga �a��ic�y�� E���p��<br />
8 H. varla �ipahi�����<br />
Hy���psychi�a��<br />
- occulta-����p�� E���p���� ���va��<br />
9 Hydropsyche kebab �a��ic�y ����h�� ��as��� ����h��as�<br />
T�����y<br />
instabilis-����p�� E���p��<br />
10 H. sinopensis �ipahi�����<br />
Psych��yii�a��<br />
- Instabilis-����p�� E���p��<br />
11 Psychomyia mengensis �ipahi����� W��s��� s���h T�����y P. pusilla Fa��ici�s�� E���p��<br />
12 P. dadayensis �ipahi����� W��s��� s���h T�����y P. pusilla Fa��ici�s�� E���p��<br />
13 Tinodes yuecelaskini �ipahi����� - T. valvatus �a��y��v�� Ca�cas�s��<br />
T�����y�� ���va��<br />
<strong>Ferrantia</strong> • 55 / 2008
F. Sipahiler Zoogeographical characteristics of the <strong>Trichoptera</strong> Fauna of Turkey<br />
No North western Turkey<br />
Distribution in<br />
Close relatives<br />
endemics<br />
B�achyc�����i�a��<br />
Turkey<br />
and their distribution<br />
14 Micrasema mencilis �ipahi�����<br />
�i����phi��i�a��<br />
- M. bifoliatum �a��y��v�� Ca�cas�s<br />
1� Drusus bayburti Ça�i� N���h��as��� ��as��� D. caucasicus U�������� Ca�cas�s�� ����h<br />
s���h���� T�����y<br />
��as� T�����y<br />
16 Drusus demirsoyi Ça�i� - D. hackeri �a��ic�y�� ����h w��s� T�����y<br />
17 D. hackeri �a��ic�y - D demirsoyi �ipahi������� ����h w��s�<br />
T�����y<br />
18 D. muchei ilgazensis �ipahi����� - D. muchei kazdagensis �ipahi������� w��s�<br />
T�����y<br />
19 Limnephilus ponticus �c�ach��a� R���i��s II-VII -<br />
20 Chaetopteryx nalanae �ipahi����� - -<br />
21 Psilopteryx turcicus Ça�i� - -<br />
22 P. t. aladagensis �ipahi�����<br />
����ic�s���a�i�a��<br />
- -<br />
23 Oecismus monedula pi�����i<br />
�a��ic�y<br />
�a��a�a R���i�� O. monedula Ha������ E���p��<br />
24 Schzopelex rhamnes �a��ic�y<br />
B���a��i�a��<br />
- S. cachetica �a��y��v�� Ca�cas�s<br />
2� Beraeamyia devrekensis<br />
- B. kamberlera �a��ic�y & �ipahi������� w��s�<br />
�ipahi�����<br />
T�����y<br />
26 Ernodes abanticus Ça�i� - E. anatolicus�� c�����a�� ��a����ia<br />
27 E. dirginensis �ipahi�����<br />
���p��c���i�a��<br />
- E.digitatus �a��y��v�� Ca�cas�s<br />
28 Oecetis brignolii �a��ic�y - N�� ��vi�����<br />
a��s� ��vi����� �ha� s���� ��a���s i� �h�� �a��� Dis��ic�<br />
w����� 90-110 � hi�h��� �ha� �h�� p���s����-�ay ����v����s.<br />
�i�i��a���y�� s��v���a�� ��a���s i� �h�� ����h a�� ��as�<br />
��a����ia a�� �h�� a�jac���� ����i��s w����� hi�h�����<br />
��.�. Va� �a��� was 80 ��� a�� U��iy�� �a��� i�<br />
I�a� was 110 � hi�h��� �ha� �h�� p���s����-�ay ����v����<br />
�E������ 1979�. I� �his way�� �a�y ��a���s a�� �h�� �iv���<br />
sys����s w����� c�����c���� �� ��ach ��h����� s� �ha� �h��<br />
����h���� fa��a hav�� f���� a ������ �� �is��i�����<br />
through the south. After the end of the pluvial<br />
p���i��s�� a� �h�� ����i��i�� �f �h�� H����c������� �h��<br />
��a���s �������a���� f��� �h��s�� a���as�� which ca�s��� �h��<br />
���s���c�i�� �f �h�� fa��as i� �h��s�� a���as�� s���� �f<br />
�h��� f���� s�a������� a���as i� �h�� Ta���s �����ai�s<br />
i� �h�� s���h. ���v���a�� ���a�p����s f�� �h��s�� sp��ci��s<br />
a��� �iv��� ������w.<br />
1 - �p��ci��s�� which a��� wi�����y �is��i������ i� �h��<br />
Pa��a��a�c�ic�� a��� a��s� f���� ���i�a����y i� �h��<br />
s�a��i�� wa����s �f T�����y; �h��s�� a��� Ecnomus<br />
tenellus Ra������ Oecetis ochracea C���is�� Athripsodes<br />
longispinosus a�� Ceraclea senilis. E. tenellus Ra����<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
is f���� i� �h�� ��a���s �f �a��� Dis��ic� i� s���h����<br />
��a����ia �Ka�a�i��� E�i��i� a�� B��ys��hi� ��a���s���<br />
a�� i� �h�� ��a���s �f �h�� ����h���� pa�� �f T�����y<br />
���a���� I���i��� �a�yas a�� B��a�ay ��a���s��� f����<br />
i� Hi�fa���i Da� ���a� ���a�a�� si�i��a� �� Oecetis<br />
ochracea C���is�� which is f���� i� �h�� ��a���s �f<br />
����h���� T�����y�� i�c����i�� Hi�fa���i Da� a�� i�<br />
�h�� ��a���s �f �a��� Dis��ic�. I� is f���� ��������s��y i�<br />
E�i��i� �a���. This sp��ci��s �cc�pi��s a ��a���� a���a i�<br />
E���p�� �h����h �h�� c�����a�� �sia�� ��� is ��� f����<br />
i� �h�� ����i�����a���a� p���i�s���as ��a��ic�y�� 1983�.<br />
�a��� Dis��ic� i� s���h���� T�����y is �h�� s���h����<br />
��i�i� �f i�s �is��i���i��. ���s� Holocentropus picicornis<br />
����ph���s�� which sh�ws h���a�c�ic �is��i���i�� a��<br />
f���� i� �a�y c�����i��s i� E���p�� i�c����i��<br />
�ca��i�avia�� is f���� i� �w� ��a���s i� w��s�����<br />
pa�� �f ��a����ia ���a�� �a��� a�� Ka�a�i� �a������<br />
���achi�� �� �h�� ����h���� pa�� �f Ta���s �����ai�s<br />
��ipahi������� 2003�. I� �h�� Ta���s �����ai�s�� i� was<br />
f���� i� ����y ���� p��ac�� i� D������ö�� �����ai��� i� a<br />
s�a���� a��pi��� ��a��� a� 23�0 � a���i�����.<br />
105
F. Sipahiler Zoogeographical characteristics of the <strong>Trichoptera</strong> Fauna of Turkey<br />
106<br />
2 - �p��ci��s�� which hav�� a ��a���� a���a i� ����h����<br />
E���p�� �� �is��i����� �h����h �h�� ����h�� hav��<br />
s�a���� a���a i� s���h���� T�����y �� a� ����as� �h��<br />
c���s�� �����a�iv��s ��iv�� �h�����. ����� �f s�ch sp��ci��s<br />
a��� f���� i� c���� s����a�s a�� hav�� a s�a���� a���a<br />
i� �h�� ����h���� s���p��s �f �h�� Ta���s �����ai�s.<br />
F�� ���a�p������ Anabolia anatolica �ipahi������� which is<br />
�h�� ��iq��� sp��ci��s �f �h�� �����s Anabolia i� T�����y��<br />
��iv��s i� ���� s���c�� sp�i���� �f which �h�� wa����<br />
temperature was measured 9.9 ºC in August. The<br />
sp��ci��s was ��� f���� i� �h�� ��h��� sp�i��s i� �h��<br />
s�������i�� a���as �ha� a��s� hav�� c���� wa����. Th��<br />
c���s�� �����a�iv�� sp��ci��s is Anabolia laevis Zetterstedt<br />
f���� i� ����h���� E���p��. Ecclisopteryx dalecarlica<br />
K������a�i �D��si�a��� �is��i�����s i� E���p�� f���<br />
�ca��i�avia �h����h �h�� Ba���a�s a�� ���c������<br />
f��� T�����y i� �a��a�a ����i�� ��ipahi������� 1999���<br />
is f���� a��s� i� �h�� ����h���� s���p��s �f Ta���s<br />
�����ai�s i� s���h���� T�����y.<br />
Phryganea grandis � has a ��a���� a���a i� E���p���� �h��<br />
vica�i��s s��sp��ci��s P. grandis serti �ipahi����� is<br />
f���� i� �h�� �a��� Dis��ic� i� s���h���� T�����y; ��<br />
�h�� sp��ci��s�� which is ��a������y �is��i������ i� E���p����<br />
has c���s�� �����a�iv��s i� T�����y ��.�. Rhyacophila polonica<br />
�c�ach��a��� �cc�pi��s a ��a���� a���a i� E���p���� c���s��<br />
�����a�iv�� sp��ci��s Rhyacophila osellai �a��ic�y is f����<br />
i� ����h���� a�� s���h���� T�����y ����� sp��ci��s��<br />
which hav�� s�a������� a���a i� E���p���� f���� a��s� i�<br />
a s�a������� a���a i� �h�� w��s����� �� s���h���� T�����y;<br />
��.�. Drusus botosaneanui K��a�s�i f���� i� �h��<br />
Ba���a�s; has a s�a���� a���a i� �h�� �����a� �����ai�s<br />
i� s���h���� T�����y ��ipahi������� 1999�. Th�� ��h���<br />
���a�p���� f�� s�ch sp��ci��s is Rhyacophila fischeri<br />
B���sa���a���� which has a �����a�iv�� s�a������� a���a<br />
i� �h�� Ba���a�s �R���a�ia�� B����a�ia�� G�����c�� a��<br />
Y���s��avia��� f���� i� s���hw��s����� T�����y.<br />
3 - Dis��i���i��s �f s���� �f �h�� sp��ci��s �f<br />
G���ss�s��a�i�a�� i� T�����y a��� p���a���y a�<br />
���a�p���� f�� Pa�����- ����i�����a���a� �yp�� �f<br />
distribution (Malicky, 1988:2). The family is<br />
���p���s������� i� T�����y �y 19 sp��ci��s�� 9 �f which<br />
a��� f���� i� �h�� ����i�����a���a� R���i�� wi�h 6<br />
�������ics. Agapetus hadimensis �ipahi������� Agapetus<br />
selgensis �ipahi����� i� �h�� s���h���� ��a����ia a��<br />
Agapetus altineri �ipahi����� i� c�����a�� ��a����ia<br />
hav�� �����a�iv��s i� �h�� ����i�����a���a� c�����i��s.<br />
I� ����hw��s����� ��a����ia 6 sp��ci��s �cc���� ���h<br />
s���h���� a�� ����hw��s����� fa��a has hi�h<br />
p���c����a��� �f �������ics �66 %�. N���h��as�����<br />
��a����ia ����i�� has � sp��ci��s ��w� �f which a���<br />
�������ics��� �f which �w� sp��ci��s�� Glossosoma<br />
capitatum �a��y��v a�� Agapetus caucasicus<br />
Fig. 9: Distributions of some species of the family Glossosomatidae in Turkey and the Caucasus.<br />
<strong>Ferrantia</strong> • 55 / 2008
F. Sipahiler Zoogeographical characteristics of the <strong>Trichoptera</strong> Fauna of Turkey<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Fig. 10: Distributions of the species of the genus Psychomyia in the western part of Anatolia.<br />
�a��y��v �is��i����� �h����h �h�� w��s����� a��<br />
s���h���� ��a����ia a�� ���va���� f���� a��s� i�<br />
Cyp��s a�� Rh����s �Fi�.9�. O�h��� sp��ci��s �f �h��<br />
fa�i��y hav�� a ��i�i���� �is��i���i��. Th�� ��a������y<br />
�is��i������ sp��ci��s Agapetus caucasicus is ��� f����<br />
i� �h�� is���a���� Ca�i��i R���i�� �����i����� a��v����<br />
�h�� �is��i���i��s �f �h�� sp��ci��s c����� ��� �h�� ���s����<br />
�f �h�� p�s� ���acia�� ���pa�si�� f��� �h�� ���f���� a���a<br />
i� �h�� Ca�cas�s.<br />
I� �h�� w��s��� 6 sp��ci��s a��� f����. ����� �h���<br />
Agapetus delicatulus �c�. is f���� i� �h�� Ba���a�s��<br />
I����ia� P���i�s���a a�� B�i�ai� a�� Agapetus episkopi<br />
�a��ic�y�� i� G�����c�� �B���sa���a�� & �a��ic�y��<br />
1978�. B��h sp��ci��s a��� ��� f���� i� �h�� ��as�<br />
a�� ����h��as����� T�����y. Th�� �������ic sp��ci��s<br />
Synagapetus anatolicus Ça�i� has a��s� a si�i��a� �yp��<br />
�f �is��i���i���� f���� i� �h�� w��s����� pa�� �f T�����y<br />
a�� ��� f���� i� c�����a�� a�� ��as� ��a����ia.<br />
4 - Th�� sp��ci��s �f �h�� �����s Psychomyia<br />
�Psych��yii�a����� which a��� wi�����y �is��i������<br />
i� �h�� �iv���s a�� s����a�s �f T�����y sh�w a�<br />
i�������s�i�� �is��i���i��. Psychomyia mengensis<br />
�ipahi������� cha�ac����i����� �y �h�� ����� spi��� �� �h�� ��p<br />
�f �h�� pha�����s�� f���� i� �h�� w��s����� pa�� �f T�����y��<br />
f������wi�� c����ai� �iv��� sys����s a�� s����a�s�� whi����<br />
�h�� ���i�h����i�� �iv��� sys���� is �cc�pi��� �y �h��<br />
��h��� sp��ci��s ��ipahi������� 200��. �y�pa��y �cc��s<br />
����y i� �w� p��ac��s i� ����hw��s����� pa�� �f T�����y.<br />
P. mengensis �ipahi����� is f���� ����y i� �w� s����a�s<br />
�a�����y�� i� �h�� s���h i� Dü���� �����a� ���a� ���a��ya<br />
a�� i� s���hw��s����� T�����y a�� i� �h�� ��i���a�y<br />
�f ����������s Riv���.<br />
I� ����hw��s����� T�����y �his sp��ci��s a��s� �cc��s<br />
i� c����ai� s����a�s a�� �iv���s�� ��.�. O�ha�����i Riv���<br />
i� �h�� w��s� a�� P��s�� �����a��� which is �h��<br />
��i���a�y �f a�jac���� �iv��� �asi� �a�a�ya �Fi�. 10�.<br />
I� �h�� ��h��� ��i���a�i��s �f �a�a�ya Riv��� i�ha�i�s<br />
Psychomyia pusilla Fabricius. In Aladağlar-<br />
Köroğlu Mountains the sources of two streams<br />
are found, one of which, namely Aladağ Stream,<br />
is found on the southern slopes of Aladağlar<br />
�����ai�s�� is �h�� ��i���a�y �f �a�a�ya Riv����� �h��<br />
��h����� G�������� �����a��� is f���� �� �h�� ����h����<br />
slopes of Köroğlu mountains and flows down to<br />
Fi��y�s Riv���. P. pusilla occur in Aladağ Stream,<br />
�h�� ��i���a�y �f �a�a�ya Riv����� whi���� i� G��������<br />
�����a��� �h�� ��i���a�y �f Fi��y�s Riv����� i�ha�i�s P.<br />
mengensis�� ��i��� �h�� ��h��� ��i���a�i��s �f �h�� �iv���<br />
�asi�. I� �his cas���� sp��ci��s �is��i������ i� s��v���a��<br />
�iv��� �asi�s is ��� a c��s��q����c�� �f �h�� c��ssi�� �f<br />
�h�� wa����sh���s ��� �h�� ���s���� �f �h�� �isp���sa�� a��<br />
the modifications of the riverine nets (Banarescu,<br />
1990�� 1991�. Th�� app��a�a�c�� �f �h�� �a��i���s ���i��<br />
the past geological times caused the modifications<br />
107
F. Sipahiler Zoogeographical characteristics of the <strong>Trichoptera</strong> Fauna of Turkey<br />
108<br />
Fig. 11: Distribution of the species of the genus Leptocerus in Turkey.<br />
�f �h�� �iv��� sys����s�� ���s����i�� i� �h�� cha���� �f �h��<br />
�asi� �f �h�� �iv���. Wh��� �h�� �a��i���s �isapp��a� �h��<br />
sp��ci��s a��� f���� sy�pa��ica����y.<br />
� - I� T�����y�� �h�� sp��ci��s �f �h�� Leptocerus<br />
interruptus ����p is ���p���s������� �y �h����� sp��ci��s.<br />
Leptocerus interruptus Fa��ici�s�� cha�ac����i����� �y<br />
asy������ica�� p�������a�i��s �f s�������� 10�� �f<br />
which �h�� �i�h� ���� is s�a���� a�� p�i����� a� �h�� ap�����<br />
is �is��i������ i� E���p�� a�� T�����y ��� ��s� �f<br />
�h�� �����a���� sp��ci��s a��� f���� i� s���h��as����� �sia.<br />
I� is f���� i� T�����y �a�y p��ac��s i� �h�� s���h����<br />
a�� ����h���� T�����y. Th�� c���s����y �����a���� sp��ci��s<br />
L. aksu �ipahi����� a�� L. savur �ipahi������� ���h hav��<br />
p�i�i�iv�� f��a�����s i� �h�� �a���� ����i�a��ia i� havi��<br />
�������� p�������a�i��s �f s�������� 10�� a��� f���� i�<br />
s���h���� ��a����ia�� L. aksu is f���� sy�pa��ica����y<br />
wi�h L. interruptus i� �h�� Ta���s �����ai�s. Th��<br />
�hi�� sp��ci��s L. savur is f���� a����s� 1000 �� ��as�<br />
�f �his a���a �Fi�. 11�. Ta���s �����ai�s i� s���h����<br />
T�����y is �h�� c������� �f ��i�i� �f �his sp��ci��s ����p��<br />
i� havi�� �w� p�i�i�iv�� sp��ci��s.<br />
References<br />
���i��a��� �. & ���i��va E. 199�. - �a��� s�a��� �f �h��<br />
���v�����p����� �f P����-Caspia�. P��c. I��.<br />
�y�p. O� �h�� G�������y �f �h�� B��ac� ���a R���i����<br />
���a�a�� 119-122.<br />
Ba�a���sc� P. 1990. - Z��������aphy �f �h�� F���sh<br />
Wa����s. V���. 1�� ����a V�����a��� Wi��s�a������ �11 pp.<br />
Ba�a���sc� P. 1991. - Z��������aphy �f �h�� F���sh<br />
Wa����s. V���. V���. 2�� 2�� ����a ����a V�����a��� V�����a��� Wi��s�a������ Wi��s�a������ 1091 pp pp.<br />
Ba��a�� P.C. 198�. - �� a����a���� ch��c�-��is� �f �h��<br />
T�ich�p����a �f B�i�ai� a�� I�����a��. E��. Ga��.��<br />
36:31-45.<br />
B���sa���a�� �. 1992. - T�ich�p����a �f ���va��.<br />
Fa��a Pa��a��s�i�a�� Th�� Is�a���� �ca����y �f<br />
�ci���c��s a�� H��a�i�i��s�� J����sa������� 291 pp.<br />
B���sa���a�� �. & �a��ic�y H. 1978. - T�ich�p����a.<br />
T�ich�p����a.<br />
T�ich�p����a.<br />
In: Illies J. (ed): Limnofauna Europaea: 333-<br />
359. 2. Aufl., Fisher: Stuttgart.<br />
<strong>Ferrantia</strong> • 55 / 2008
F. Sipahiler Zoogeographical characteristics of the <strong>Trichoptera</strong> Fauna of Turkey<br />
Cianficconi F. 2002. - Th�� �hi�� ��is� �f I�a��ia�<br />
T�ich�p-����a �1990-2000�. P��c. 10 �h I��.�y�p.<br />
<strong>Trichoptera</strong>. Nova Suppl. Ent., Keltern, 15:349-<br />
3�8.<br />
Cianficconi F., Moretti G.P. & Tucciarelli F. 1997.<br />
-Italian <strong>Trichoptera</strong> fauna: zoological consid-<br />
���a�i��s. P��c�����i��s �f �h�� 8 �h I������a�i��a��<br />
�y�p�si�� �� T�ich�p����a�� �i��iap���is�� 199���<br />
Ohi� Bi�����ica�� ���v��y P����ica�i���� pp. 69-7�.<br />
E���� O. 1979. - Dördüncü Çağ (Quarterner) Jeoloji<br />
v�� j������f����jisi�i� a�a çi���i�����i. Di�� v�� Ta�ih-<br />
Coğr. Fak. Fa�. Yay. �ay. 289�� 289, 68 pp.<br />
K�����h�va I. 1986. - The fauna of caddis flies of<br />
the Caucasus. Latvijas Entomologs, 29:60-84.<br />
K��a�s�i K. 1980. -� c����i���i�� �� �h��<br />
���w�������� �f T�ich�p����a �I�s��c�a� �f �h��<br />
Caucasus. Acta Zool. Bulg. 14:32-48.<br />
K��a�s�i K. 198�. - T�ich�p����a�� ������ipa��pia.<br />
Fa��a B����a�ica 1��� �ci���c�� �ca����y �f<br />
Bulgaria, Sofia, 243 pp.<br />
K��a�s�i K. 1988. - T�ich�p����a I������ipa��pia.<br />
Fa��a B����a�ica 19�� �ci���c�� �ca����y �f<br />
B����a�ia�� 3�4 pp.<br />
Lüttig G. & Steffens P. 1976. - E�p��a�a���y E�p��a�a���y N����s N����s f�� f��<br />
�h�� Pa�����������aphic ����as �f T�����y f��� �h��<br />
O��i��c����� �� �h�� P����is��c�����. B�����sa�s�a��� B�����sa�s�a��� fü� fü�<br />
Geowissenschaften und Rohrstoffe, Hannover,<br />
64 pp.<br />
�a��ic�y H. 1983. - Chorological patterns and biome<br />
�yp��s �f E���p��a� T�ich�p����a a�� ��h��� f���shwater<br />
insects. Arch. Hydrobiol. 96,2:223-244.<br />
Malicky H. 1988: 1. - Drusus concolor KE�PNY��<br />
1908 �T�ich�p����a�� �i����phi��i�a����� ���a<br />
sp��ci��s. E���������isch�� Nach�ich���� ���<br />
Berichte, 32:65-68.<br />
Malicky H. 1988: 2. - �p����� ���� Eis����i� i�<br />
���� T�ich�p�������fa��a E���pas �I�s��c�a��<br />
<strong>Trichoptera</strong>). Riv. Idrobiol., 27, 2-3:247-297.<br />
�a��ic�y H. 1999. - Ei��� a���a��isi������ �is��� ����<br />
österreichischen Köcherfliegen (<strong>Trichoptera</strong>).-<br />
Braueria, 26:31-40.<br />
Malicky H. 1997. Neue Köcherfliegen aus dem<br />
�i�a��� �T�ich�p����a�� �i����phi��i�a��-Ph�y�aneidae).<br />
Entomol.Z., 2:60-63.<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
�a��ic�y H. 2002. - Einige Köcherfliegen<br />
�T�ich�p����a� a�s F�a�����ich ��� I�a��i���.<br />
Entomofauna, Ansfelden 23,1:1-12.<br />
�a��ic�y H. & Cha��a�a�a������� P. 1996. - N�����<br />
Köcherfliegen aus Thailand. Arbeit Nr. 19 über<br />
thailändische Köcherfliegen. Entomologische<br />
Berichte Luzern, 36:119-128.<br />
�a��ic�y H. & �ipahi����� F. 1984. - � fa��is�ic s��v��y<br />
of the caddisflies (<strong>Trichoptera</strong>) of Turkey. 207-<br />
212�� i� ���s�� J. C. ������� F����h I������a�i��a��<br />
�y�p�si�� �� T�ich�p����a�� ����i��s E�����-<br />
����ica�� V������� 30�� D�. W. J��� P����ish���s�� Th��<br />
Ha����.<br />
�a��ic�y H. & �ipahi����� F. 1993. - Köcherfliegen<br />
�T�ich�p����a� a�s ���� Tü����i �i� B�������������<br />
zu weiteren Mediterranen Köcherfliegen.- Mitt.<br />
�chw��i��. E��.G��s. 66:457-478.<br />
�c�ach��a� R. 1874-1880. - � ������aphic<br />
���visi�� a�� sy��psis �f �h�� T�ich�p����a �f<br />
�h�� E���p��a� fa��a. �������� J�h� va� V���s���<br />
B�����i� F�i�����a������� & ��h��� �23 pp.<br />
���y W. 2004. - B��i��a� ���� T�ich�p����a-Fa��a<br />
������i���s ��� ���s I�a� �T�ich�p����a�. E�����logische<br />
Nachrichten und Berichte, 48:81-87. 81-87.<br />
�i���ay���i �. & �a��ic�y H. 2002. - �� �p�a����<br />
check-list of caddisflies (Insecta, <strong>Trichoptera</strong>)<br />
f��� I�a��� wi�h ���w ���c���s. Z������y i� �h��<br />
Middle East 26:163-168.<br />
�ipahi����� F. 1996. - ����i��s �� �h�� T�ich�p����a<br />
fa��a �f s���h���� ��a����ia. E�����fa��a<br />
(Ansfelden) 17, 16:293-309.<br />
�ipahi����� F. 200�. - � R��visi�� �f �h�� �����s<br />
Psychomyia �a����i�������� 1829 i� T�����y<br />
�T�ich�p����a�� Psych��yii�a���.- �q�a�ic I�s��c�s��<br />
�i� p�i���.<br />
�ipahi����� F. 200�. - � ch��c���is� �f T�ich�p����a �f<br />
T�����y. 393-40��� i� i� K. Ta�i�a Ta�i�a Ta�i�a a�� a�� a�� �. �. �. R�ssi���� R�ssi���� R�ssi����<br />
����s��� 11�h I������a�i��a�� �y�p�si�� ��<br />
T�ich�p����a�� �2003�� Osa�a��� T��ai U�iv���si�y<br />
P���ss�� Ka�a�awa.<br />
�ipahi����� F.�� �a��ic�y H. 1987. - Die Köcherfliegen<br />
der Türkei (<strong>Trichoptera</strong>).- Entomofauna, 8:77-<br />
16�.<br />
109
L. Ujvárosi árosi rosi et et al. First revision of the Romanian caddisflies<br />
110<br />
First revision of the Romanian caddisflies<br />
(Insecta: <strong>Trichoptera</strong>)<br />
Part 1: Systematic checklist (updated 12/2005)<br />
Lujza Ujvárosi árosi rosi<br />
D��pa������� �f Ta�����y a�� Ec�����y<br />
�Babeş-Bolyai� �Babeş-Bolyai� Babeş-Bolyai� ş-Bolyai� -B���yai" " U�iv���si�y�� University, U�iv���si�y�� University, U�iv���si�y�� C��i�ici���� Clinicilor C��i�ici���� Clinicilor C��i�ici���� �-7 5-7 �-7 5-7 �-7<br />
3400 C���j�� R��a�ia<br />
���i��a@�i�����.���c���j.��<br />
Sabina C. Robert<br />
D��pa������� �f Hy����i�����y�� I�s�i����� �f Ec�����y<br />
U�iv���si�y �f D�is����-Ess�����<br />
D-4�117 Ess����� G����a�y<br />
sa�i�a.�������@��i-��ss���.���<br />
Peter Neu<br />
R��-K������-���. 2�� 2��<br />
D-�4634 Bi�����<br />
p������.����@��ich�p����a-�p.���<br />
http://www.trichoptera-rp.de<br />
Berthold Robert<br />
B����h���� R�������� B�����h�v���s��. 8<br />
D-46282 D��s����<br />
�����h����.�������@�-����i���.���<br />
http://www.trichoptera.de<br />
Keywords: Insecta, <strong>Trichoptera</strong>, faunistic, nomenclature, systematic, checklist, Romania, endemics<br />
Abstract<br />
The first faunistical, nomenclatorial and systematical<br />
revised checklist of the caddisflies (<strong>Trichoptera</strong>) from<br />
R��a�ia si�c�� Ci���c �1993� is p���s������� h�����. Th��<br />
sys����a�ic ch��c���is� ��w c���ai�s 266 sp��ci��s �14 a���<br />
�������ic f�� R��a�ia c�����sp���i�� �� ���3 % �f �h�� ���a��<br />
fa��a� f��� 8� �������a a�� 19 fa�i��i��s ��a�.1�. Of �h��s�� 24<br />
taxa are named for the first time. These are: Rhyacophila<br />
armeniaca G����i�-������vi�������� 1843 R.. obtusa K��apa�������<br />
1894�� Synagapetus slavorum B���sa���a���� 1960�� Hydroptila<br />
aegyptia U�������� 1963�� H. angustata ��s����y�� 1939�� H. martini<br />
�a�sha������ 1977�� Orthotrichia tragetti ��s����y�� 1930�� Hydropsyche<br />
incognita Pi�sch�� 1993�� H. peristerica B���sa���a�� &<br />
�a�i���vic�� 1968�� Polycentropus ierapetra �a��ic�y�� 1972��<br />
Lepidostoma basale �K������a�i�� 1848��� Anabolia concentrica<br />
(Zetterstedt, 1840), Anisogamus difformis ��c�ach��a���<br />
1876��� Chaetopteryx bosniaca �a�i���vic�� 19���� C. rugulosa<br />
K������a�i�� 1848�� Drusus monticola �c�ach��a��� 1878�� Hydatophylax<br />
infumatus �c�ach��a� 186��� Isogamus czarnohorensis<br />
�D��i�����i������wic���� 1912��� Limnephilus sericeus ��ay�� 1824���<br />
Melampophylax polonicus �a��ic�y�� 1990�� Potamophylax<br />
carpathicus �D��i�����i������wic���� 1912��� Stenophylax meridiorientalis<br />
�a��ic�y�� 1990�� Ceraclea albimacula �Ra������ 1842���<br />
Oecetis notata �Ra������ 1842�.<br />
O� �h�� ��h��� ha�� 31 �a�a �����i����� �y Ci���c �1993�<br />
and others have been omitted from the list.<br />
These are: Rhyacophila valkanovi B���sa���a���� 19�7��<br />
Agapetus fuscipes C���is�� 1834�� Orthotrichia melitta �a��ic�y��<br />
1976�� Wormaldia triangulifera �c�ach��a��� 1878�� Hydropsyche<br />
siltalai D���h������� 1963�� Tinodes waeneri ��i��a���s�� 17�8���<br />
Lasiocephala basalis �K������a�i�� 1848��� Anabolia nervosa<br />
�C���is�� 1834��� Annitella transilvanica �����ci�� 19�7��<br />
<strong>Ferrantia</strong> • 55 / 2008
L. Ujvárosi árosi rosi et et al. First revision of the Romanian caddisflies<br />
Asynarchus lapponicus (Zetterstedt, 1840), Chaetopteryx<br />
cissylvanica B���sa���a���� 19�9�� C. fontisdraconis<br />
B���sa���a���� 1993�� C. schmidi B���sa���a���� 19�7�� Drusus<br />
annulatus �����ph���s�� 1837��� Ecclisopteryx guttulata �Pic������<br />
1834��� Halesus rubricollis �Pic������ 1834��� Limnephilus<br />
centralis C���is�� 1834�� L. microdentatus �a��y��v�� 1913��<br />
L. politus �c�ach��a��� 186��� Melampophylax mucoreus<br />
�Ha������ 1861��� Mesophylax impunctatus �c�ach��a��� 1884��<br />
Nemotaulius punctatolineatus �R�����i�s�� 1783��� Stenophylax<br />
vibex �C���is�� 1834��� Silo nigricornis �Pic������ 1834���<br />
Athripsodes aterrimus �����ph���s�� 1836��� A. leucophaeus<br />
�Ra������ 1842��� Ceraclea alboguttata �Ha������ 1860��� C.<br />
Introduction<br />
I� �h�� ��as� ���ca���s si�c�� �h�� c�isis �f �i��iv���si�y<br />
has ������ �����a����y ���c���i����� ���s��a�ch��s�� which<br />
f�c�s��� �� hi�h q�a��i�y fa��is�ica�� �a�a�� hav��<br />
increased. The recently finalized �Fauna Europaea<br />
P��j��c�" �av�� a �aj�� c����i���i�� �� ��va���a��� �h��<br />
�i��iv���si�y �f E���p���� �as��� �ai���y �� �����ia�����<br />
records from different countries. In such projects<br />
�p�a���� i�f���a�i�� ���a��i�� wi�h a ���ca�� ��<br />
����i��a�� fa��a is a��ways w������ app���cia���� as w������<br />
as a c�i�ica�� ���visi�� �f �h�� p����ish��� i�f���a�i��<br />
f��� ��ach c�����y �as��� �� ���c������y c�������c����<br />
�a����ia��.<br />
Investigation of the caddisfly (<strong>Trichoptera</strong>) fauna<br />
has a ����� ��a�i�i�� i� R��a�ia; ��v��� �his ���s��a�ch<br />
was made with changing intensity in different<br />
periods. The first faunistical data from Romania<br />
w����� p����ish��� j�s� ���f���� �h�� ���� �f �h�� 19 �h<br />
c������y �y K��apa����� �1898�� 1899�. Th�� pap���s<br />
�� "Fa��a R����i H���a�ia��" a��s� �av�� f���h���<br />
information about the diversity of caddisfly<br />
sp��ci��s ��s���y f��� �h�� Ca�pa�hia�s ���csá�y<br />
1900; P����ác�� 1914�.<br />
Th�� �aj�� c����i���i�� �� �h�� ���w�������� �f<br />
�h�� R��a�ia� T�ich�p����a was �����iv������ �y<br />
B���sa���a���� wh� p����ish��� ��sp��cia����y ����w�����<br />
19�2 a�� 1978 a ��a���� ������� �f i�p���a��<br />
�a�����ica���� fa��is�ica�� a�� ��c�����ica�� �a�a a����<br />
�h�� �aj��i�y �f �h�� T�ich�p����a sp��ci��s �cc���i��<br />
i� R��a�ia �s���� ��i����a����� ��is� i� Ci���c 1993�. Th��<br />
first checklist of the entire fauna of the country was<br />
p����ish��� �y Ci���c i� 1993�� �as��� ��a������y �� �h��<br />
a�a��ysis �f �h�� p����ish��� ��i����a������� ��� as w������ ��<br />
��p����ish��� �a����ia�� c�������c���� �y B���sa���a����<br />
�a��ic�y a�� hi�s����f. This ��is� c���ai���� 267<br />
T�ich�p����a sp��ci��s a�� ��h��� 10 w����� �����i�������<br />
��� c��si������� as �����f��� f�� R��a�ia.<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
nigronervosa �R�����i�s�� 1783��� Erotesis baltica �c�ach��a���<br />
1877�� Oecetis intima �c�ach��a��� 1877�� Ylodes conspersus<br />
�Ra������ 1842�.<br />
I� �h�� ch��c���is� sp��ci��s a��� ����y i�c��������� if �����ia�����<br />
���c���s �f a�����s ���is�. ����� �a�a�� �a�a�� �� f�� f�� f�� which ����y ����y ����y ��a�va�� ��a�va�� ��a�va��<br />
�a�a a��� ���w��� hav�� ������ ���c������� f��� �h�� ��is�. �����<br />
changes are briefly explained. The revision is on the<br />
���� ha�� �as��� �� a ��a���� q�a��i�y �f a����� �a����ia��<br />
�ai���y c�������c���� �y �h�� a��h��s i� �h�� ��as� �hi�������<br />
y��a�s c��p�isi�� 182 sp��ci��s. B��si��� ��� ���c���� �a�a�� a����<br />
�������va�� a�� �����ia����� ��i����a����� ���f������c��s a�� �a�a f���<br />
�h�� Fa��a E���pa��a p��j��c� w����� i�c�������.<br />
Since this first summary of Romanian <strong>Trichoptera</strong><br />
several taxonomic problems have found a better<br />
s�����i�� a�� a ���� �f ���w ���c���s w����� p����ish���.<br />
Th�� ��i����a����� �a�a p����ish��� si�c�� Ci���c �1993�<br />
a��� c�i�ica����y ���vis��� a�� ����ich��� wi�h ��� ���c����<br />
���w ���c���s.<br />
In the first part of the revision of the Romanian<br />
T�ich�p����a w�� p���s���� a fa��is�ica����<br />
������c��a���ia�� a�� sys����a�ica�� ���vis��� ch��c���is�<br />
of the caddisfly species occurring in Romania. The<br />
s��c��� pa���� which wi���� ��� p����ish��� ��a������ wi����<br />
p���s���� a ����i��a��i����� a�� �p�a���� �is��i���i��<br />
�f �h�� sp��ci��s i� R��a�ia.<br />
Material and methods<br />
Th�� ch��c���is� is �as��� �� a c�i�ica�� ���visi�� �f<br />
the first summary of Romanian <strong>Trichoptera</strong><br />
p����ish��� �y Ci���c �1993� a�� �h�� fa��is�ica��<br />
�a�a p����ish��� �y B���sa���a�� �1993�� 199����<br />
Ci���c �2004��� Pa���s �2004��� Ujv�si �1994�� 199���<br />
1997a�����c�� 1998a����� 1999�� 2000�� 2002�� 2003��� Ujva��si<br />
& Chis� �1999��� Ujva��si & N����� �1996��� Ujva��si<br />
& N���a�i �1999� a�� Ujva��si ��� a��. �199��. W��<br />
hav�� a��s� �a���� i��� c��si����a�i�� �h�� i�p���a��<br />
���c���� ���visi��s�� ���c�������a�i��s p����ish��� �y<br />
B���sa���a�� �199�� a�� �a��ic�y �200�� as w������<br />
as unpublished samplings done from different<br />
����i��s i� R��a�ia ��� ����y �y �h�� a��h��s�� ���<br />
a��s� �y N���á�i �P�cs��� Pa���s �F�a��f���� a��<br />
Uh�����vich �P�cs�.<br />
I� �h�� p���s���� ��is� w�� �s�� ����y ���������ss �a�a<br />
�f a�����s. Th�����f���� a���� sp��ci��s �f which ����y<br />
larval data are known have been omitted from<br />
�h�� ch��c���is�. �s f�� �h�� �aj��i�y �f R��a�ia�<br />
T�ich�p����a sp��ci��s �h�� ������aphica�� va�ia�i��i�y<br />
111
L. Ujvárosi árosi rosi et et al. First revision of the Romanian caddisflies<br />
112<br />
�f ���ph�����ica�� pa�a�������s was ����ss s���i��� a�<br />
p�p���a�i�� ����v���� ����c��p� s���� w��� �f B���sa���a��<br />
1973�� 197��� 199�; ���y a�� B���sa���a�� 198�� w��<br />
av�i� �si�� s��sp��ci��s �a�a i� ��� ��is� f�� �h��<br />
�������.<br />
Th�� ������c��a����� a�� sys����a�ic a��a���������<br />
�f �h�� ch��c���is� f������ws �a��ic�y �200�� as was<br />
generally agreed at the first conference on faunistics<br />
a�� ����������aphy �f E���p��a� T�ich�p����a i�<br />
������������� ��� i� sh����� ��� ������ �ha� �h��<br />
senior author in some cases is of different opinion<br />
�R������ 2001�� 2004� .<br />
Results<br />
The present checklist of Romanian caddisflies<br />
�T�ich�p����a� c���ai�s 266 sp��ci��s f��� 8� �������a<br />
a�� 19 fa�i��i��s.<br />
The presence of 182 species has been confirmed<br />
i� �h�� ��as� �hi������� y��a�s �as��� �� a�����s c�������c����<br />
�ai���y �y �h�� a��h��s ��a����� wi�h * i� �h�� ��is��.<br />
Systematic checklist of<br />
Romanian <strong>Trichoptera</strong><br />
Rhyacophilidae Stephens, 1836<br />
Rhyacophila Pictet, 1834<br />
*Rhyacophila aquitanica �c�ach��a��� 1879<br />
*Rhyacophila armeniaca G����i�-������vi�������� 1843<br />
Rhyacophila cibinensis B���sa���a�� & �a�i���vic��<br />
1967<br />
Rhyacophila confinium B���sa���a���� 19�7<br />
*Rhyacophila doehleri B���sa���a���� 19�7<br />
*Rhyacophila fagarashiensis B���sa���a���� 1964<br />
*Rhyacophila fasciata Ha������ 18�9<br />
*Rhyacophila fischeri B���sa���a���� 19�7<br />
*Rhyacophila flava K��apa������� 1898<br />
*Rhyacophila furcifera K��apa������� 1904<br />
*Rhyacophila glareosa �c�ach��a��� 1867<br />
*Rhyacophila kimminsiana B���sa���a���� 19�8<br />
*Rhyacophila laevis Pic������ 1834<br />
*Rhyacophila mocsaryi K��apa������� 1898<br />
*Rhyacophila motasi B���sa���a���� 19�7<br />
*Rhyacophila nubila (Zetterstedt, 1840)<br />
*Rhyacophila obliterata �c�ach��a��� 1863<br />
*Rhyacophila obtusa K��apa������� 1894<br />
*Rhyacophila orghidani B���sa���a���� 19�2<br />
*Rhyacophila philopotamoides �c�ach��a��� 1879<br />
*Rhyacophila polonica �c�ach��a��� 1879<br />
*Rhyacophila torrentium Pic������ 1834<br />
*Rhyacophila tristis Pic������ 1834<br />
Glossosomatidae Wallengren, 1891<br />
Glossosoma Curtis, 1834<br />
*Glossosoma boltoni C���is�� 1834<br />
*Glossosoma conformis N����iss�� 1963<br />
*Glossosoma discophorum K��apa������� 1902<br />
*Glossosoma intermedium �K��apa������� 1892�<br />
Agapetus Curtis, 1834<br />
*Agapetus belareca B���sa���a���� 19�7<br />
*Agapetus delicatulus �c�ach��a��� 1884<br />
*Agapetus laniger �Pic������ 1834�<br />
*Agapetus ochripes C���is�� 1834<br />
Agapetus rectigonopoda B���sa���a���� 19�7<br />
Synagapetus McLachlan, 1879<br />
Synagapetus armatus ��c�ach��a��� 1879�<br />
Synagapetus iridipennis �c�ach��a��� 1879<br />
*Synagapetus moselyi �U�������� 1938�<br />
Synagapetus slavorum B���sa���a���� 1960<br />
Hydroptilidae Stephens, 1836<br />
Hydroptila Dalman, 1819<br />
*Hydroptila aegyptia U�������� 1963<br />
*Hydroptila angustata ��s����y�� 1939<br />
*Hydroptila forcipata �Ea����� 1873�<br />
*Hydroptila lotensis ��s����y�� 1930<br />
Hydroptila martini �a�sha������ 1977<br />
*Hydroptila occulta �Ea����� 1873�<br />
*Hydroptila pulchricornis Pic������ 1834<br />
*Hydroptila simulans ��s����y�� 1920<br />
Hydroptila sparsa C���is�� 1834<br />
Hydroptila tineoides Da���a��� 1819<br />
Hydroptila vectis C���is�� 1834<br />
Ithytrichia Eaton, 1873<br />
*Ithytrichia lamellaris Ea����� 1873<br />
Orthotrichia Eaton, 1873<br />
Orthotrichia angustella ��c�ach��a��� 186��<br />
*Orthotrichia costalis �C���is�� 1834�<br />
*Orthotrichia tragetti ��s����y�� 1930<br />
<strong>Ferrantia</strong> • 55 / 2008
L. Ujvárosi árosi rosi et et al. First revision of the Romanian caddisflies<br />
Allotrichia McLachlan, 1880<br />
*Allotrichia pallicornis �Ea����� 1873�<br />
Agraylea Curtis, 1834<br />
Agraylea multipunctata C���is�� 1834<br />
*Agraylea sexmaculata C���is�� 1834<br />
Tricholeiochiton Kloet & Hincks, 1944<br />
Tricholeiochiton fagesi �G�i�a���� 1879�<br />
Oxyethira Eaton, 1873<br />
*Oxyethira falcata �������� 1893<br />
*Oxyethira flavicornis �Pic������ 1834�<br />
Stactobiella Martynov, 1924<br />
Stactobiella risi �F���������� 1908�<br />
Stactobia McLachlan, 1880<br />
Stactobia caspersi U�������� 19�0<br />
Stactobia maclachlani Ki��i�s�� 1949<br />
Philopotamidae Stephens, 1829<br />
Wormaldia McLachlan, 1865<br />
*Wormaldia occipitalis �Pic������ 1834�<br />
*Wormaldia pulla ��c�ach��a��� 1878�<br />
Wormaldia subnigra �c�ach��a��� 186�<br />
Philopotamus Stephens, 1829<br />
*Philopotamus montanus �D���va��� 1813�<br />
*Philopotamus variegatus ��c�p���i�� 1763�<br />
Ecnomidae Uulmer, 1903<br />
Ecnomus McLachlan, 1864<br />
*Ecnomus tenellus �Ra������ 1842�<br />
Polycentropodidae Uulmer, 1903<br />
Holocentropus McLachlan, 1878<br />
Holocentropus dubius �Ra������ 1842�<br />
*Holocentropus picicornis �����ph���s�� 1836�<br />
Holocentropus stagnalis �����a��a�� 1874�<br />
Cyrnus Stephens, 1836<br />
*Cyrnus crenaticornis �K������a�i�� 18�9�<br />
*Cyrnus trimaculatus �C���is�� 1834�<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Polycentropus Curtis, 1835<br />
*Polycentropus excisus K��apa������� 1894<br />
*Polycentropus flavomaculatus �Pic������ 1834�<br />
*Polycentropus ierapetra �a��ic�y�� 1972<br />
*Polycentropus irroratus C���is�� 183�<br />
Polycentropus schmidi N�va� & B���sa���a���� 196�<br />
Neureclipsis McLachlan, 1864<br />
*Neureclipsis bimaculata ��i��a���s�� 17�8�<br />
Plectrocnemia Stephens, 1836<br />
*Plectrocnemia brevis �c�ach��a��� 1871<br />
*Plectrocnemia conspersa �C���is�� 1834�<br />
*Plectrocnemia kisbelai B���sa���a���� 1967<br />
*Plectrocnemia minima K��apa������� 1899<br />
Psychomyiidae Curtis, 1835<br />
Lype McLachlan, 1878<br />
*Lype phaeopa �����ph���s�� 1836�<br />
*Lype reducta �Ha������ 1868�<br />
Psychomyia Latreille, 1829<br />
*Psychomyia pusilla �Fa��ici�s�� 1781�<br />
Tinodes Curtis, 1834<br />
Tinodes kimminsi �y���a�� 1962<br />
Tinodes pallidulus �c�ach��a��� 1878<br />
*Tinodes polifurculatus B���sa���a���� 19�6<br />
Tinodes raina B���sa���a���� 1960<br />
*Tinodes rostocki �c�ach��a��� 1878<br />
Tinodes unicolor �Pic������ 1834�<br />
Hydropsychidae Curtis, 1835<br />
Diplectrona Westwood, 1840<br />
Diplectrona atra �c�ach��a��� 1878<br />
Cheumatopsyche Wallengren, 1891<br />
*Cheumatopsyche lepida �Pic������ 1834�<br />
Hydropsyche Pictet, 1834<br />
*Hydropsyche angustipennis �C���is�� 1834�<br />
Hydropsyche botosaneanui �a�i���vic�� 1966<br />
*Hydropsyche bulbifera �c�ach��a��� 1878<br />
*Hydropsyche bulgaromanorum �a��ic�y�� 1977<br />
*Hydropsyche contubernalis �c�ach��a��� 186�<br />
Hydropsyche emarginata Navas�� 1923<br />
*Hydropsyche fulvipes �C���is�� 1834�<br />
113
L. Ujvárosi árosi rosi et et al. First revision of the Romanian caddisflies<br />
114<br />
*Hydropsyche incognita Pi�sch�� 1993<br />
*Hydropsyche instabilis �C���is�� 1834�<br />
*Hydropsyche modesta Navas�� 192�<br />
Hydropsyche ornatula �c�ach��a��� 1878<br />
*Hydropsyche pellucidula �C���is�� 1834�<br />
*Hydropsyche peristerica B���sa���a�� & �a�i���vic��<br />
1968<br />
*Hydropsyche saxonica �c�ach��a��� 1884<br />
Hydropsyche sinuata B���sa���a�� & �a�i���vic��<br />
1966<br />
*Hydropsyche tabacarui B���sa���a���� 1960<br />
Phryganeidae Leach, 1815<br />
Agrypnia Curtis, 1835<br />
*Agrypnia pagetana C���is�� 183�<br />
Agrypnia picta K������a�i�� 1848<br />
*Agrypnia varia �Fa��ici�s�� 1793�<br />
Hagenella Martynov, 1924<br />
*Hagenella clathrata �K������a�i�� 1848�<br />
Oligostomis Kolenati, 1848<br />
Oligostomis reticulata ��i��a���s�� 1761�<br />
Oligotricha Rambur, 1842<br />
*Oligotricha striata ��i��a���s�� 17�8�<br />
Trichostegia Kolenati, 1848<br />
Trichostegia minor �C���is�� 1834�<br />
Phryganea Linnaeus, 1758<br />
Phryganea bipunctata R�����i�s�� 1783<br />
*Phryganea grandis �i��a���s�� 17�8<br />
Brachycentridae Ulmer, 1903<br />
Brachycentrus Curtis, 1834<br />
Brachycentrus maculatus �F���c��y�� 178��<br />
Brachycentrus montanus K��apa������� 1892<br />
*Brachycentrus subnubilus C���is�� 1834<br />
Micrasema McLachlan, 1876<br />
*Micrasema minimum �c�ach��a��� 1876<br />
Uenoidae Iwata, 1927<br />
Thremma McLachlan, 1876<br />
Thremma anomalum �c�ach��a��� 1876<br />
Goeridae Ulmer, 1903<br />
Goera Stephens, 1829<br />
*Goera pilosa �Fa��ici�s�� 177��<br />
Lithax McLachlan, 1876<br />
*Lithax niger �Ha������ 18�9�<br />
*Lithax obscurus �Ha������ 18�9�<br />
Silo CURTIS, 1830<br />
*Silo graellsi Pic������ 186�<br />
*Silo pallipes �Fa��ici�s�� 1781�<br />
*Silo piceus �B�a������ 18�7�<br />
Lepidostomatidae Ulmer, 1903<br />
Lepidostoma Rambur, 1842<br />
*Lepidostoma basale �K������a�i�� 1848�<br />
*Lepidostoma hirtum �Fa��ici�s�� 177��<br />
Crunoecia McLachlan, 1876<br />
Crunoecia irrorata �C���is�� 1834�<br />
Crunoecia monospina B���sa���a���� 1960<br />
Limnephilidae Kolenati, 1848<br />
Dicosmoecinae Schmid, 1955<br />
Ironoquia Banks, 1916<br />
*Ironoquia dubia �����ph���s�� 1837�<br />
Apataniinae Wallengren, 1886<br />
Apatania Kolenati, 1848<br />
*Apatania carpathica �ch�i��� 19�4<br />
Drusinae Banks, 1916<br />
Ecclisopteryx Kolenati, 1848<br />
*Ecclisopteryx dalecarlica K������a�i�� 1848<br />
*Ecclisopteryx madida ��c�ach��a��� 1867�<br />
Drusus Stephens, 1837<br />
*Drusus biguttatus �Pic������ 1834�<br />
*Drusus brunneus K��apa������� 1898<br />
Drusus buscatensis B���sa���a���� 1960<br />
Drusus carpathicus D��i�����i������wic���� 1911<br />
*Drusus discolor �Ra������ 1842�<br />
Drusus monticola �c�ach��a��� 1876<br />
<strong>Ferrantia</strong> • 55 / 2008
L. Ujvárosi árosi rosi et et al. First revision of the Romanian caddisflies<br />
*Drusus romanicus �����ci & B���sa���a���� 19�3<br />
*Drusus tenellus �K��apa������� 1898�<br />
*Drusus trifidus �c�ach��a��� 1868<br />
Limnephilinae Kolenati, 1848<br />
Limnephilini Kolenati, 1848<br />
Anabolia Stephens, 1837<br />
*Anabolia brevipennis �C���is�� 1834�<br />
*Anabolia concentrica (Zetterstedt, 1840)<br />
*Anabolia furcata B�a������ 18�7<br />
Anabolia laevis (Zetterstedt, 1840)<br />
Glyphotaelius Stephens, 1837<br />
*Glyphotaelius pellucidus �R�����i�s�� 1783�<br />
Grammotaulius Kolenati, 1848<br />
*Grammotaulius nigropunctatus �R�����i�s�� 1783�<br />
*Grammotaulius nitidus ��ü��������� 1764�<br />
Limnephilus Leach, 1815<br />
*Limnephilus affinis C���is�� 1834<br />
*Limnephilus auricula C���is�� 1834<br />
Limnephilus binotatus C���is�� 1834<br />
*Limnephilus bipunctatus C���is�� 1834<br />
*Limnephilus coenosus C���is�� 1834<br />
*Limnephilus decipiens �K������a�i�� 1848�<br />
*Limnephilus extricatus �c�ach��a��� 186�<br />
*Limnephilus flavicornis �Fa��ici�s�� 1787�<br />
*Limnephilus flavospinosus �����i��� 1874�<br />
Limnephilus fuscicornis Ra������ 1842<br />
*Limnephilus griseus ��i��a���s�� 17�8�<br />
*Limnephilus hirsutus �Pic������ 1834�<br />
*Limnephilus ignavus �c�ach��a��� 186�<br />
*Limnephilus incisus C���is�� 1834<br />
*Limnephilus lunatus C���is�� 1834<br />
Limnephilus nigriceps (Zetterstedt, 1840)<br />
Limnephilus rhombicus ��i��a���s�� 17�8�<br />
Limnephilus sericeus ��ay�� 1824�<br />
*Limnephilus sparsus C���is�� 1834<br />
*Limnephilus stigma C���is�� 1834<br />
*Limnephilus vittatus �Fa��ici�s�� 1798�<br />
Chaetopterygini Hagen, 1858<br />
Annitella Klapalek, 1907<br />
*Annitella lateroproducta �B���sa���a���� 19�2�<br />
*Annitella obscurata ��c�ach��a��� 1876�<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Chaetopterygopsis Stein, 1874<br />
Chaetopterygopsis maclachlani ����i��� 1874<br />
Chaetopterygopsis sisestii B���sa���a���� 1961<br />
Chaetopteryx Stephens, 1837<br />
*Chaetopteryx biloba B���sa���a���� 1960<br />
*Chaetopteryx bosniaca �a�i���vic�� 19��<br />
Chaetopteryx major �c�ach��a��� 1876<br />
Chaetopteryx polonica D��i�����i������wic���� 1889<br />
*Chaetopteryx sahlbergi �c�ach��a��� 1876<br />
Chaetopteryx rugulosa K������a�i�� 1848<br />
Chaetopteryx subradiata K��apa������� 1907<br />
Psilopteryx Stein, 1874<br />
*Psilopteryx curviclavatus B���sa���a���� 19�7<br />
Psilopteryx psorosa �K������a�i�� 1860�<br />
Stenophylacini Schmid, 1955<br />
Acrophylax Brauer, 1867<br />
*Acrophylax vernalis D��i�����i������wic���� 1912<br />
Allogamus Schmid, 1955<br />
*Allogamus auricollis �Pic������ 1834�<br />
*Allogamus dacicus ��ch�i��� 19�1�<br />
*Allogamus uncatus �B�a������ 18�7�<br />
Anisogamus McLachlan, 1875<br />
Anisogamus difformis ��c�ach��a��� 1876�<br />
Chionophylax Schmid, 1951<br />
Chionophylax czarnohoricus �D��i�����i������wic���� 1911�<br />
Chionophylax mindszentyi �ch�i��� 19�1<br />
Halesus Stephens, 1836<br />
*Halesus digitatus ��ch�a���� 1781�<br />
*Halesus tessellatus �Ra������ 1842�<br />
Hydatophylax Wallengren, 1891<br />
*Hydatophylax infumatus ��c�ach��a��� 186��<br />
Isogamus Schmid, 1955<br />
Isogamus aequalis �K��apa������� 1907�<br />
Isogamus czarnohorensis �D��i�����i������wic���� 1912�<br />
Isogamus lineatus K��apa������� 1903<br />
Melampophylax Schmid, 1955<br />
Melampophylax nepos ��c�ach��a��� 1880�<br />
Melampophylax polonicus �a��ic�y�� 1990<br />
115
L. Ujvárosi árosi rosi et et al. First revision of the Romanian caddisflies<br />
116<br />
Micropterna Stein, 1874<br />
*Micropterna lateralis �����ph���s�� 1837�<br />
*Micropterna nycterobia �c�ach��a��� 187�<br />
*Micropterna sequax �c�ach��a��� 187�<br />
Micropterna testacea �G�����i��� 1789�<br />
Parachiona Thomson, 1891<br />
*Parachiona picicornis �Pic������ 1834�<br />
Potamophylax Wallengren, 1891<br />
*Potamophylax carpathicus �D��i�����i������wic���� 1912�<br />
*Potamophylax cingulatus �����ph���s�� 1837�<br />
*Potamophylax Potamophylax jungi ���y�� 1976<br />
*Potamophylax latipennis �C���is�� 1834�<br />
*Potamophylax luctuosus (Piller & Mitterpacher,<br />
1783�<br />
*Potamophylax millenii �K��apa������� 1898�<br />
*Potamophylax nigricornis �Pic������ 1834�<br />
*Potamophylax pallidus �K��apa������� 1899�<br />
*Potamophylax rotundipennis �B�a������ 18�7�<br />
Rhadicoleptus Wallengren, 1891<br />
*Rhadicoleptus alpestris �K������a�i�� 1848�<br />
Stenophylax Kolenati, 1848<br />
*Stenophylax meridiorientalis �a��ic�y�� 1980<br />
Stenophylax mitis �c�ach��a��� 187�<br />
*Stenophylax permistus �c�ach��a��� 189�<br />
Sericostomatidae Stephens, 1836<br />
Oecismus McLachlan, 1876<br />
*Oecismus monedula �Ha������ 18�9�<br />
Sericostoma Latreille, 1825<br />
*Sericostoma personatum �Ki��y & �p���c���� 1826�<br />
*Sericostoma flavicorne �ch���i������ 184�<br />
Notidobia Stephens, 1829<br />
Notidobia ciliaris ��i��a���s�� 1761�<br />
Odontoceridae Wallengren, 1891<br />
Odontocerum Leach, 1815<br />
*Odontocerum albicorne ��c�p���i�� 1763�<br />
*Odontocerum hellenicum �a��ic�y�� 1972<br />
Helicopsychidae Ulmer, 1906<br />
Helicopsyche Siebold, 1856<br />
Helicopsyche bacescui O��hi�a� & B���sa���a����<br />
19�3<br />
Beraeidae Wallengren, 1891<br />
Beraea Stephens, 1833<br />
Beraea maurus �C���is�� 1834�<br />
*Beraea pullata �C���is�� 1834�<br />
Beraeamyia Mosely, 1930<br />
Beraeamyia hrabei �ay����� 1937<br />
Beraeamyia schmidi B���sa���a���� 1960<br />
Beraeodes Eaton, 1867<br />
Beraeodes minutus ��i��a���s�� 1761�<br />
Ernodes Wallengren, 1891<br />
*Ernodes articularis �Pic������ 1834�<br />
*Ernodes vicinus ��c�ach��a��� 1879�<br />
Leptoceridae Leach, 1815<br />
Adicella McLachlan, 1877<br />
Adicella altandroconia B���sa���a�� & N�va��� 196�<br />
*Adicella filicornis �Pic������ 1834�<br />
Adicella reducta ��c�ach��a��� 186��<br />
Adicella syriaca U�������� 1907<br />
Triaenodes McLachlan, 1865<br />
Triaenodes bicolor �C���is�� 1834�<br />
Ylodes Milne, 1934<br />
*Ylodes kawraiskii ��a��y��v�� 1909�<br />
*Ylodes simulans �Tj�������� 1929�<br />
Parasetodes McLachlan, 1880<br />
Parasetodes respersella �Ra������ 1842�<br />
Mystacides Berthold, 1827<br />
*Mystacides azurea ��i��a���s�� 1761�<br />
*Mystacides longicornis ��i��a���s�� 17�8�<br />
*Mystacides nigra ��i��a���s�� 17�8�<br />
Athripsodes Billberg, 1820<br />
Athripsodes albifrons ��i��a���s�� 17�8�<br />
*Athripsodes bilineatus ��i��a���s�� 17�8�<br />
<strong>Ferrantia</strong> • 55 / 2008
L. Ujvárosi árosi rosi et et al. First revision of the Romanian caddisflies<br />
Athripsodes cinereus �C���is�� 1834�<br />
*Athripsodes commutatus �R�s��c��� 1874�<br />
Ceraclea Stephens, 1829<br />
*Ceraclea albimacula �Ra������ 1842�<br />
Ceraclea annulicornis �����ph���s�� 1836�<br />
Ceraclea aurea �Pic������ 1834�<br />
*Ceraclea dissimilis �����ph���s�� 1836�<br />
Ceraclea fulva �Ra������ 1842�<br />
Ceraclea riparia �����a��a�� 1874�<br />
*Ceraclea senilis �B�����is������ 1839�<br />
Setodes Rambur, 1842<br />
Setodes hungaricus U�������� 1908<br />
*Setodes punctatus �Fa��ici�s�� 1793�<br />
Setodes viridis �F���c��y�� 178��<br />
Leptocerus Leach, 1815<br />
*Leptocerus interruptus �Fa��ici�s�� 177��<br />
*Leptocerus tineiformis C���is�� 1834<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Oecetis McLachlan, 1877<br />
*Oecetis furva �Ra������ 1842�<br />
*Oecetis lacustris �Pic������ 1834�<br />
*Oecetis notata �Ra������ 1842�<br />
*Oecetis ochracea �C���is�� 182��<br />
*Oecetis testacea �C���is�� 1834�<br />
Oecetis tripunctata �Fa��ici�s�� 1793�<br />
Table 1: Proportion of families for the <strong>Trichoptera</strong> fauna of Romania.<br />
Families<br />
Number of<br />
species 2005<br />
Th�� p��p���i�� �f �h�� fa�i��i��s f�� �h�� T�ich�p����a<br />
fa��a is sh�w� i� �a����� 1. Th�� c��p�si�i�� is<br />
v���y si�i��a� �� �ha� ���sc�i���� �y Ci���c �1993���<br />
a���h���h �� �a�a �a���� 20 %� �f �h�� fa��a hav��<br />
cha����� c��pa���� wi�h Ci���c �1993�. This is<br />
a hi�h �a��� �f cha���� i� �h�� sp��ci��s c��p�si�i��<br />
between the first and this second checklist. For<br />
G����a�y i� c��pa�is���� ���� �f �h�� ��s� w������<br />
i�v��s�i�a���� c�����i��s �f E���p���� �h�� �a��� �f<br />
cha���� i� �h�� sp��ci��s c��p�si�i�� i� �h�� sa���<br />
�i��� is c����a���y ������w 10 % �f �h�� fa��a �R������<br />
��p����ish��� �a�a�. �� �h�� hi�h �a��� �f cha���� is<br />
Number of<br />
species Ciubuc<br />
(1993)<br />
Percentage 2005<br />
Percentage<br />
Ciubuc (1993)<br />
� � % %<br />
Rhyac�phi��i�a�� 23 21 8��6 7��9<br />
G���ss�s��a�i�a�� 13 13 4��9 4��9<br />
Hy���p�i��i�a�� 24 21 9��0 7��9<br />
Phi���p��a�i�a�� � � 1��9 1��9<br />
Ec���i�a�� 1 1 0��4 0��4<br />
P���yc������p��i�a�� 1� 14 ���6 ���2<br />
Psych��yi�a�� 9 10 3��4 3��7<br />
Hy���psychi�a�� 18 16 6��8 6��0<br />
Ph�y�a���i�a�� 9 9 3��4 3��4<br />
B�achyc�����i�a�� 4 4 1��� 1���<br />
U����i�a�� 1 1 0��4 0��4<br />
G����i�a�� 6 7 2��3 2��6<br />
���pi��s���a�i�a�� 4 4 1��� 1���<br />
�i����phi��i�a�� 87 89 32��7 33��3<br />
����ic�s���a�i�a�� 4 4 1��� 1���<br />
O�����c���i�a�� 2 2 0��8 0��8<br />
H����ic�psychi�a�� 1 1 0��4 0��4<br />
B���a��i�a�� 7 7 2��6 2��6<br />
���p��c���i�a�� 33 38 12��4 14��2<br />
Summe: 266 267 100 100<br />
117
L. Ujvárosi árosi rosi et et al. First revision of the Romanian caddisflies<br />
118<br />
a s����� hi�� �p�� �ha� �h�� fa��a �f �h�� c�����y<br />
is ��� s� i�����siv����y i�v��s�i�a���� ���i�� ��w a�� a<br />
���� �f ���w �isc�v���i��s c����� ��� �a��� i� �h�� f������.<br />
W�� ��s�i�a��� �ha� �i�i�a����y a ������� �f 10-20<br />
sp��ci��s wi���� ��� ������c���� f�� �h�� c�����y ��sp��cia����y<br />
i� �h�� fa�i��y Hy���p�i��i�a��.<br />
Comments on the revised<br />
checklist of the Romanian<br />
<strong>Trichoptera</strong><br />
I� �h�� f������wi�� �h�� cha��i���s cha��i���s �ss �ha� �ha� �ha� �ha� �ha� happ������ happ������ happ������ happ������ happ������<br />
since the publishing of the first checklist by Ciubuc<br />
(1993) are briefly explained.<br />
a) Caddisfly taxa that have been added to the<br />
Romanian fauna since Ciubuc (1993)<br />
F��� �h�� ac��a�� ch��c���is� a ������� �f 246 �a�a<br />
w����� a�����a�y ��is���� i� Ci���c �1993�. ���v���������<br />
a��i�i��a�� sp��ci��s a��� �����i����� i� �����ia�����<br />
pap���s �ha� w����� p����ish��� si�c�� Ci���c �1993�.<br />
Tw� sp��ci��s a��� ��is���� ����y i� �h�� Fa��a E���pa��a<br />
�a�a�as��. O��� sp��ci��s is �����i����� f�� R��a�ia<br />
in this publication for the first time. Five taxa<br />
a��� ���w ���ca�s�� �f ������c��a���ia��/sys����a�ica��<br />
cha����s. ���������h��� 24 �a�a a��� ���c������ h����� f��<br />
the first time compared to Ciubuc (1993). These<br />
taxa are:<br />
1. Rhyacophila armeniaca: in the Fauna Europaea<br />
�a�a�as�� �Ba��a�� 200�� �h�� sp��ci��s is ��is����<br />
f�� R��a�ia. Ci���c �1993� s�a���� �ha�<br />
�h�� p���s���c�� �f �h�� sp��ci��s f�� R��a�ia is<br />
�����f���. C��c����i�� �a��ic�y �200�� �h�� �a���<br />
is not conspecific with R.. torrentium as s�a����<br />
by Botosaneanu (1995). A first brief revision of<br />
s���� �a����ia�� ���p�si���� ������ R.. torrentium<br />
in the collection of the first author revealed<br />
�h�� p���s���c�� �f R.. armeniaca i� �h�� Eas�����<br />
Ca�pa�hia�s.<br />
2. Rhyacophila obtusa: cited from Botosaneanu (1993).<br />
3. Synagapetus slavorum: cited from Botosaneanu<br />
�1993�� 199��.<br />
4. Hydroptila aegyptia: cited from Botosaneanu (1995).<br />
�. Hydroptila angustata: cited from Ujvárosi (1994),<br />
B���sa���a�� �199��.<br />
6. Hydroptila martini: cited from Botosaneanu (1993).<br />
7. Orthotrichia tragetti: cited from Ciubuc (2004).<br />
I� 2002 a�� 2003 �h�� sp��ci��s was ca��h� i� �h��<br />
Da����� D�����a �Ca�a���a��� Chi��c�� E�isa��a��<br />
G����va�� �a��i�c�� �i��a 23�� ���i�hi���� a� ��i�h�<br />
i� hi�h �������s.<br />
8. Hydropsyche incognita: cited from Malicky (1999)<br />
a�� i� 2004 a��s� c�������c���� �y �. Ba��i�� �C���j�<br />
a�� P. N��� f��� �h�� Eas����� Ca�pa�hia�s a��<br />
T�a�sy��va�ia� D��p���ssi�� �s���� a��s� p����ica�i��<br />
�f Ba��i�� i� �his v��������.<br />
9. Hydropsyche peristerica: New for the Romanian<br />
fa��a!<br />
Sampling data are listed here for the first time:<br />
1 �a������ 3� f���a����s�� 21.VII. 2004�� �����. ��� ����. N�����<br />
�ac�������� �is��ic� B�as�v�� Eas����� Ca�pa�hia�s��<br />
s����a� ���a� ��a� 1� a� Ba�a���ca�� 960 � a.s.��.��<br />
light trap, col. Neu, GPS coordinates: 9410021<br />
�042190.<br />
10 �a����s�� 7 f���a����s�� 23.VII .2004�� �����. ��� ����.<br />
N����� Baia �p�i���� �p�i���� �� �is��ic� �is��ic� �is��ic� �a�a�����s�� �a�a�����s�� �a�a�����s�� Eas����� Eas����� Eas�����<br />
Ca�pa�hia�s�� p��a������ 9�0 � a.s.��.�� ��i�h� ��ap��<br />
col. Neu, GPS coordinates: 8475293 5298451<br />
7 f���a����s�� 2�.VII. 2004�� �����. ��� ����. N����� Va����a<br />
Vi�����i�� �is��ic� Bis��i�a-Nasa���� Eas�����<br />
Ca�pa�hia�s�� s����a��� 630 � a.s.��.�� ��i�h� ��ap�� c���.<br />
Neu, GPS coordinates: 8562509 5260471<br />
10. Polycentropus ierapetra ierapetra: this species was<br />
mentioned for the first time by Ujvárosi<br />
�1994��� ��� �h�� si������ f���a���� c�������c���� i�<br />
�h�� Eas����� Ca�pa�hia�s ������� ��� �� ��� P.<br />
irroratus �Ujv�si 199��. Th�� sp��ci��s was a�ai�<br />
briefly noted in Ujvárosi (2003), but without<br />
c��p������� sa�p��i�� �a�a. Th��s�� a��� p����ish���<br />
here for the first time: 1 male, 4 females,<br />
1�.VII.1992�� �����. Uh�����vics�� f��� H������<br />
s����a��� Bai���� H�������� �is��ic� Ha��hi�a��<br />
Eastern Carpathians, identified by Nogradi<br />
& Uherkovich confirmed the presence for the<br />
c�����y ��w.<br />
11. Lepidostoma basale: in Ciubuc (1993) the<br />
sp��ci��s is �����i����� ������ Lasiocephala basalis<br />
�K������a�i�� 1848�. C��c����i�� �a��ic�y �200��<br />
�h�� �����s Lasiocephala C�s�a�� 18�7 has ���c������y<br />
������ sy���y�i����� wi�h Lepidostoma.<br />
12. Anabolia concentrica: cited from Ujvárosi (1995)<br />
a�� Ujv�si ��� a��. �199��.<br />
13. Anisogamus difformis: cited from Botosaneanu<br />
�1993�.<br />
<strong>Ferrantia</strong> • 55 / 2008
L. Ujvárosi árosi rosi et et al. First revision of the Romanian caddisflies<br />
14. Chaetopteryx bosniaca: cited from Botosaneanu<br />
�199���� wh����� i� is �����i����� as Chaetopteryx<br />
bosniaca cissylvanica B���sa���a���� 19�9�� ���<br />
f�� acc��p�a�c�� �f s��sp��ci��s s�a��s s���� a��s�<br />
�a��ic�y �200��.<br />
1�. Chaetopteryx rugulosa: Ciubuc (1993) mentioned<br />
i� ������ Chaetopteryx schmidi B���sa���a����<br />
19�7. �a��ic�y �200�� has �����c��� C. schmidi ��<br />
a s��sp��ci��s �f C. rugulosa.<br />
16. Drusus monticola: cited from Botosaneanu (1993)<br />
17. Hydatophylax infumatus: cited from Ujvárosi<br />
�2003�. Th�� f������wi�� c��p������� sa�p��i�� �a�a<br />
are given here for the first time:<br />
10 �a����s�� � f���a����s�� 11. VII. 2002�� �����. ��� ����.<br />
Ujvárosi, Voşlobeni, Senetea stream, �Mlaştina<br />
După Luncă� nature reserve, district Harghita,<br />
Eas����� Ca�pa�hia�s�� 740 ��� ��i�h� ��ap�� c���.<br />
Ujv�si.<br />
3 �a����s�� 13. VII. 2002�� �����. ��� ����. Ujv�si��<br />
Voşlobeni, Senetea stream, district Harghita,<br />
Eas����� Ca�pa�hia�s�� 740 ��� a� ��i�h��� c���.<br />
Ujv�si.<br />
18. Isogamus czarnohorensis: species listed in<br />
Fa��a E���pa��a �a�a�as�� �Ba��a�� 200�� f��<br />
R��a�ia.<br />
�cc���i�� �� Fisch��� �1969� �h�� �a��� was<br />
��i�i�a����y ���sc�i���� as Anisogamus aequalis va�.<br />
czarnohorensis D��i�����i������wic���� D��i�����i������wic���� 1912�� 1912�� f��� f��� �h�� �h�� �h��<br />
C��a���h��a �����ai�s�� Eas����� Ca�pa�hia�s��<br />
which a��� ���ay ���vi���� �y �h�� ������� ����w�����<br />
R��a�ia a�� U��ai�a. ��y ��y ��h��� ��h��� ��h��� ��h��� i�f���a�i��<br />
i�f���a�i��<br />
i�f���a�i��<br />
i�f���a�i��<br />
a���� �h�� �cc������c�� a�� �is��i���i�� �f �h��<br />
sp��ci��s i� R��a�ia is �����w� �� �� �h�� �h�� �h�� a��h��s a��h��s a��h��s<br />
a� �h�� ������� a�� w����� ��� hi�h��y app���cia����<br />
�h�����f����.<br />
19. Limnephilus sericeus: cited from Botosaneanu (1993�.<br />
20. Melampophylax polonicus: cited from<br />
B���sa���a�� �199��.<br />
21. Potamophylax carpathicus: cited from Ujvárosi<br />
�1998��.<br />
22. Stenophylax meridiorientalis: Botosaneanu (1995)<br />
s�a���� �ha� ����y S. vibex meridiorientalis �a��ic�y��<br />
1980 �cc��s i� R��a�ia. H����� w�� f������w �h��<br />
���c�������a�i�� f��� �a��ic�y �1980�� 200��<br />
wh� ����a���� S. meridiorientalis as ���a sp��ci��s.<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
23. Ceraclea albimacula: in Ciubuc (1993) the species<br />
is �����i����� ������ Ceraclea alboguttata �Ha������<br />
1860�. C��c����i�� �a��ic�y �200�� C. alboguttata<br />
is a sy���y� �f C. albimacula.<br />
24. Oecetis notata: cited from Ujvárosi (1995)<br />
b) Caddisfly taxa formerly mentioned for the<br />
Romanian fauna, but are now omitted<br />
� ������� �f 31 �a�a�� which w����� ��is���� i� �h��<br />
ch��c���is� �f Ci���c �1993� �� i� ��h��� p����ica�i��s��<br />
are now omitted from the Romanian fauna,<br />
���ca�s�� �� �����ia����� ���c���s a��� ���w� �� ���ca�s��<br />
of misidentifications, nomenclatorial changes and<br />
�a�����ica�� ���visi��s p����ish��� i� �h�� ��as� ���ca���<br />
(Botosaneanu 1995; Malicky 2005). These taxa are:<br />
1. Rhyacophila valkanovi Botosaneanu, 1957: it<br />
is s�a���� �y B���sa���a�� �199�� �ha� i� is a<br />
sy���y� �f R. torrentium.<br />
2. Agapetus fuscipes Curtis, 1834: listed in Ciubuc<br />
�1993��� ��� w�� c��si���� i� as ������������y �����f�����<br />
���ca�s�� �h�� ����y ���w� ���c���s p����ish��� �y<br />
B���sa���a�� �19�2� a��� �as��� ����y �� ��a�va��<br />
identification. Concerning the Fauna Europaea<br />
�a�a�as�� �Ba��a�� 200�� �h�� sp��ci��s is a��s�<br />
�����w� f��� a���� ���i�h���i�� c�����i��s �f<br />
R��a�ia ���c��p� H���a�y. Th����� i� �cc��s ����y<br />
i� �h�� ��s� ����h���� a�� w��s����� pa��s �f �h��<br />
c�����y �N���a�i & Uh�����vich 2002��� which<br />
�i�i�a����y a��� 100 �� fa� f��� �h�� R��a�ia�<br />
������� wi�h �h�� G���a� H���a�ia� P��ai� i�<br />
����w�����.<br />
3. Orthotrichia melitta Malicky, 1976: record<br />
c��si������� as �����f��� �y B���sa���a�� �199��.<br />
Th�� sp��ci��s is a��s� �� �������� ��is���� f�� �h��<br />
Da����� D�����a �y Ci���c �2004�.<br />
4. Wormaldia triangulifera McLachlan, 1878: the<br />
sp��ci��s was �����i����� i� Ujv�si �1997a�<br />
�as��� �� ���� ��i����a����� �a�a�� ��� Ci���c �1993�<br />
a�����a�y s�a���� �ha� a���� f������ ci�a�i��s w����� ���<br />
c�����c�.<br />
�. Hydropsyche siltalai Doehler, 1963: Ujvárosi<br />
�199�� s�a���� �ha� �h�� ��������i�a�i�� p����ish���<br />
�y Ujv�si �1994� was ��� c�����c�. Th�� si������<br />
�a���� c�������c���� i� �h�� Eas����� Ca�pa�hia�s<br />
������� ��� �� ��� H. instabilis. Th�� ���c��� �f �h��<br />
sp��ci��s i� Ujva��si & Chis� �1999� is �as��� ����y<br />
�� �h�� ��������i�a�i�� �f ��a�va�� a�� �h�����f����<br />
classified as doubtful. The species is mentioned<br />
i� �h�� Fa��a E���pa��a �a�a�as�� �Ba��a�� 200��<br />
119
L. Ujvárosi árosi rosi et et al. First revision of the Romanian caddisflies<br />
120<br />
p���a���y �as��� �� �h�� ���c���s i� Ujva��si �1994�<br />
a��/�� Ujva��si & Chis� �1999��� ��� w�� �����i��v��<br />
�his ����������s�� ���ca�s�� a�y ��h��� �����ia�����<br />
s���c�� �f �a�a f�� �h�� �cc������c�� i� R��a�ia<br />
is ���a����y �����w� �� �s. ���s� f��� �h�� ���w�<br />
�is��i���i�� �f H. siltalai i� E���p�� i� is ����i�����y<br />
�ha� i� �cc��s i� R��a�ia. C��c����i�� �h��<br />
Fa��a E���pa��a �a�a�as�� �Ba��a�� 200�� i� is<br />
�����w� f��� a���� ���i�h���i�� c�����i��s �f<br />
R��a�ia ���c��p� H���a�y. Th����� i� �cc��s ����y<br />
i� �h�� ��s� ����h���� a�� w��s����� pa��s �f �h��<br />
c�����y �N���a�i & Uh�����vich 2002��� which<br />
�i�i�a����y a��� 1�0 �� fa� f��� �h�� R��a�ia�<br />
������� wi�h �h�� G���a� H���a�ia� P��ai� i�<br />
����w�����.<br />
6. Tinodes waeneri (Linnaeus, 1758): record<br />
c��si������� as �����f��� �y B���sa���a�� �199��.<br />
7. Lasiocephala basalis (Kolenati, 1848):<br />
c��c����i�� �a��ic�y �200�� a���� sp��ci��s �f �����s<br />
Lasiocephala hav�� ������ ��a�sf������� �� �h�� �����s<br />
Lepidostoma.<br />
8. Anabolia nervosa (Curtis, 1834): record<br />
c��si������� as �����f��� �y B���sa���a�� �199��.<br />
�s ca� ��� s����� i� Ci���c �1993� a���� ���w�<br />
���c���s a��� �as��� ����y �� ��a�va��.<br />
9. Annitella transilvanica Murgoci, 1957:<br />
�a�����ica�� a�� ������c��a���ia�� s�a��s �f �h��<br />
�a��� is s�i���� ��c����a� �B���sa���a�� 199��. �a��ic�y<br />
�200�� ����a���� �h�� �a��� as a� i���������ia���<br />
f��� ����w����� A. lateroproducta a�� Annitella<br />
chomiacensis �D��i�����i������wic���� 1908�.<br />
10. Asynarchus lapponicus (Zetterstedt, 1840): cited<br />
i� Ujv�si �1998��� 2002���� ��� a ���vis�� sh�w�����<br />
�ha� a���� sp��ci����s c�������c���� f��� �h�� Eas�����<br />
Ca�pa�hia�s ����������� �� A. brevipennis.<br />
11. Chaetopteryx cissylvanica Botosaneanu, 1959:<br />
�a��ic�y �1994� sy���y�i����� �h�� �a��� wi�h C.<br />
bosniaca; ��a���� B���sa���a�� �199�� �����i����� i�<br />
as C. bosniaca cissylvanica; ��� f�� acc��p�a�c�� �f<br />
s��sp��ci��s s�a��s s���� a��s� �a��ic�y �200��.<br />
12. Chaetopteryx fontisdraconis Botosaneanu, 1993:<br />
�a��ic�y �200�� s�a���� �ha� �h�� �a��� is a va�i���y<br />
�f C. bosniaca.<br />
13. Chaetopteryx schmidi Botosaneanu, 1957:<br />
�a��ic�y �200�� has �����c��� i� �� a s��sp��ci��s��<br />
Chaetopteryx rugulosa schmidi B���sa���a����<br />
19�7�� i� �h�� C. rugulosa-c��p�����.<br />
14. Drusus annulatus (Stephens, 1837): record<br />
c��si������� as �����f��� �y B���sa���a�� �199��.<br />
����� ���w� ���c���s a��� �as��� ����y �� ��a�va��.<br />
1�. Ecclisopteryx guttulata (Pictet, 1834): record<br />
c��si������� as �����f��� �y B���sa���a�� �199��.<br />
F������ ���c���s a��� �as��� ����y �� ��a�va�� �s����<br />
Ci���c 1993�.<br />
16. Halesus rubricollis (Pictet, 1834): record<br />
c��si������� as �����f��� �y B���sa���a�� �199��.<br />
F������ ���c���s a��� �as��� ����y �� ��a�va�� �s����<br />
Ci���c 1993�.<br />
17. Limnephilus centralis Curtis, 1834: record<br />
c��si������� as �����f��� �y B���sa���a�� �199��.<br />
�s ca� ��� s����� i� Ci���c �1993� a���� f������<br />
���c���s a��� �as��� ����y �� ��a�va��.<br />
18. Limnephilus microdentatus Martynov, 1913:<br />
ci���� i� Ujv�si �1998���� ��� �h�� si������ f���a����<br />
c�������c���� f��� �h�� W��s����� P��ai� ����������� �� L.<br />
flavicornis.<br />
19. Limnephilus politus McLachlan, 1865: record<br />
c��si������� as �����f��� �y B���sa���a�� �199��.<br />
F������ ���c���s a��� �as��� ����y �� ��a�va�� �s����<br />
Ci���c 1993�.<br />
20. Melampophylax mucoreus (Hagen, 1861):<br />
B���sa���a�� �199�� s�a���� �ha� a���� sp��ci����s<br />
��������i�a���� i� R��a�ia as M. mucoreus<br />
�������� �� M. polonicus.<br />
21. Mesophylax impunctatus McLachlan, 1884:<br />
���c��� c��si������� as �����f��� �y B���sa���a��<br />
�199��. �s ca� ��� s����� i� Ci���c �1993� a����<br />
f������ ���c���s a��� �as��� ����y �� ��a�va��.<br />
22. Nemotaulius punctatolineatus (Retzius, 1783):<br />
���c��� c��si������� as �����f��� �y B���sa���a��<br />
�199��. F������ ���c���s a��� �as��� ����y �� ��a�va��<br />
�s���� Ci���c 1993�.<br />
23. Stenophylax vibex (Curtis, 1834): Botosaneanu<br />
�199�� s�a���� �ha� ����y S. vibex meridiorientalis<br />
�a��ic�y�� 1980 �cc��s i� R��a�ia�� ���<br />
�a��ic�y �200�� ����a���� �h�� �a��� as a sp��ci��s��<br />
S. meridiorientalis. �� a���� ���c���s f���<br />
Ci���c �1993� c��c����i�� S. vibex vibex a��<br />
S. vibex meridiorientalis sh����� ���f��� �� S.<br />
meridiorientalis.<br />
24. Silo nigricornis (Pictet, 1834): listed in Ciubuc<br />
�1993��� ��� w�� c��si���� i� as ������������y �����f�����<br />
���ca�s�� �h�� ����y ���w� ���c���s p����ish���<br />
�y B��a �1943-4�� a�� �����ci & ������sc�<br />
<strong>Ferrantia</strong> • 55 / 2008
L. Ujvárosi árosi rosi et et al. First revision of the Romanian caddisflies<br />
(1955) are based only on larval identification.<br />
C��c����i�� �h�� Fa��a E���pa��a �a�a�as��<br />
�Ba��a�� 200�� �h�� sp��ci��s is a��s� �����w�<br />
f��� a���� ���i�h���i�� c�����i��s �f R��a�ia<br />
���c��p� H���a�y. Th����� i� �cc��s ����y i� �h��<br />
��s� ����h���� a�� w��s����� pa��s �f �h�� c�����y<br />
�N���a�i & Uh�����vich 2002��� which �i�i�a����y<br />
a��� 100 �� fa� f��� �h�� R��a�ia� ������� wi�h<br />
�h�� G���a� H���a�ia� P��ai� i� ����w�����.<br />
2�. Athripsodes aterrimus (Stephens, 1836): record<br />
c��si������� as �����f��� �y B���sa���a�� �199��.<br />
F������ ���c���s a��� �as��� ����y �� ��a�va�� �s����<br />
Ci���c 1993�. F�� �his sp��ci��s �h����� is a hi�h<br />
cha�c�� �ha� i� a��s� �cc��s i� R��a�ia�� ���ca�s��<br />
i� H���a�y i� is ���w� f��� �h�� ���a��s/�����s<br />
�iv���-����i�� a� �h�� �i���c� ������� �� R��a�ia<br />
�s���� N���a�i & Uh�����vich 2002�.<br />
26. Athripsodes leucophaeus (Rambur, 1842): record<br />
c��si������� as �����f��� �y B���sa���a�� �199��.<br />
27. Ceraclea alboguttata (Hagen, 1860): Malicky<br />
�200�� s�a���� �ha� �h�� �a��� is a sy���y� �f C.<br />
albimacula.<br />
28. Ceraclea nigronervosa (Retzius, 1783): record<br />
c��si������� as �����f��� �y B���sa���a�� �199��.<br />
29. Erotesis baltica McLachlan, 1877: record<br />
c��si������� as �����f��� �y B���sa���a�� �199��.<br />
30. Oecetis intima McLachlan, 1877: record<br />
c��si������� as �����f��� �y B���sa���a�� �199��.<br />
31. Ylodes conspersus (Rambur, 1842): record<br />
c��si������� as �����f��� �y B���sa���a�� �199��.<br />
Th�� �a��� Phryganea ochrida �a��ic�y�� 197� was<br />
�����i����� as a ���w sp��ci��s f�� R��a�ia �y Ci���c<br />
�2004� i� his p����ica�i�� a���� �h�� T�ich�p����a �f<br />
�h�� Da����� D�����a R��s���v���� ��� Wi��i�s �1998� has<br />
sy���y�i����� P. ochrida wi�h Phryganea grandis<br />
���f����. �a��ic�y �200�� ����s��� a������ wi�h Wi��i�s<br />
�1998� a�� �����s�a���ish��s �h�� �a��� as Phryganea<br />
grandis ochrida ��a��ic�y�� 197��. U��i�� a ���visi��<br />
�f �h�� P. grandis-c��p����� is c����c������ w�� f������w<br />
�a��ic�y �200�� a�� �h�����f���� �h�� s��sp��ci��s is ���<br />
��is���� i� �h�� ch��c���is�.<br />
Th�� ��is�i�� �f �h�� sp��ci��s Rhyacophila hirticornis<br />
�c�ach��a��� 1879�� Halesus radiatus �C���is�� 1834� i�<br />
Ujv�si & Chis� �1999��� Silo nigricornis i� Chis�<br />
�2002� a�� Rhyacophila aurata B�a������ 18�7 i� R������<br />
& C�����a�-Ba�a��c �200�� is �as��� ����y �� ��a�va��<br />
��������i�a�i�� a�� �h�����f���� �h��y a��� ��� i�c�������<br />
i� �h�� ch��c���is� �f �h�� T�ich�p����a �f R��a�ia.<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Comparison with the data of<br />
the Fauna Europaea project<br />
� c��pa�is�� �f �h�� ���vis��� T�ich�p����a ch��c���is�<br />
p���s������� h����� wi�h �h�� �a�a f�� R��a�ia i� �h��<br />
�a�a �as�� �f �h�� Fa��a E���pa��a p��j��c� sh�ws �h��<br />
f������wi�� ���s����s. Thi������� sp��ci��s a��� �issi�� i�<br />
the data base for Romania and should be added:<br />
Anisogamus difformis, Chaetopteryx bosniaca, Drusus<br />
monticola, Hydatophylax infumatus, Hydropsyche<br />
peristerica, Hydroptila martini, Orthotrichia tragetti,<br />
Limnephilus sericeus, Melampophylax polonicus,<br />
Polycentropus ierapetra, Rhyacophila obtusa,<br />
Sericostoma flavicorne, Stenophylax meridiorientalis.<br />
As well as thirteen species should be added in<br />
the database so also six species should be omitted<br />
from the list of Romania in the Fauna Europaea<br />
data base. These are:<br />
Agapetus fuscipes, Chaetopteryx fontisdraconis,<br />
Hydropsyche siltalai, Melampophylax mucoreus, Silo<br />
nigricornis, Stenophylax vibex.<br />
Endemic species<br />
R���a��i�� �i��iv���si�y ���� i�p���a�� fac��� is ��<br />
���w�� which sp��ci��s a��� �������ic f�� �h�� �����i���y<br />
�f a s�a���. F�� s�ch sp��ci��s ��v��� �� a w�����wi���<br />
����v���� �h�� s�a��� is ���a����y ���sp��si����� c��c����i��<br />
�h��i� p�����c�i�� a�� c��s���va�i��.<br />
Ta�i�� i��� acc���� �h�� ���w� E���p��a� �is��i-<br />
���i�� �f �h�� T�ich�p����a �cc���i�� i� R��a�ia<br />
as ��c��������� i� Ba��a�� �200���� B���sa���a��<br />
B���sa���a��<br />
�197�� a�� a�� Wi�����-�a�s��� Wi�����-�a�s��� �2004� �2004� �h�� �h�� f������wi�� f������wi��<br />
f��������� sp��ci��s a��� �������ic f�� �h�� �����i���y �f<br />
Romania:<br />
Allogamus dacicus, Chaetopteryx biloba, Drusus<br />
brunneus�� D. buscatensis, Hydropsyche sinuata,<br />
Isogamus lineatus, Potamophylax jungi, P. millenii,<br />
Rhyacophila cibinensis, R. confinium, R. doehleri, R.<br />
fagarashiensis, R. kimminsiana, R. motasi.<br />
O� �h�� sp��ci��s ����v���� �h��s�� a��� ���3 % �f �h�� ���a��<br />
T�ich�p����a fa��a �f R��a�ia. �cc���i�� ��<br />
Wi�����-�a�s��� �2004� �his is �f ����i�� �a��i�����<br />
i� E���p���� wh����� �h�� hi�h��s� �a���s �f �������is�<br />
a��� f���� i� �h�� I����ia� P���i�s���a �34 %��� G�����c��<br />
�2� %� a�� �h�� I�a��ia� fa��a �20 %�.<br />
121
L. Ujvárosi árosi rosi et et al. First revision of the Romanian caddisflies<br />
122<br />
Comparison of the Romanian<br />
<strong>Trichoptera</strong> fauna with other<br />
European states<br />
Th�� R��a�ia� T�ich�p����a fa��a is c��pa���� wi�h<br />
��h��� s������c���� E���p��a� s�a���s �y �h�� �s�� �f �h��<br />
B�ay-C���is i����� �f si�i��a�i�y �as��� �� p���s���c��/<br />
a�s���c�� �a�a. Th�� ������� �f sp��ci��s is c�����c����<br />
after Malicky (2005). The results are shown in<br />
�a����� 3. I� is v���y i�������s�i���� �ha� �h�� hi�h��s�<br />
��������� �f si�i��a�i�y ���is�s wi�h ����va�ia �77��2<br />
%��� P���a�� �72��6 %� a�� H���a�y �72��0 %��� s�a���s<br />
which a��s� sha��� ����a� pa��s �f �h�� Ca�pa�hia�<br />
�����ai� Ra������ a���h���h ����va�ia a�� P���a��<br />
a��� ��� �i���c� ���i�h���s �f R��a�ia. F�� B����a�ia��<br />
which is a �i���c� ���i�h����� wi�h 69��9 % �h�� ���������<br />
of similarity is a little bit smaller. It is also notable,<br />
�ha� �h�� fa��is�ic si�i��a�i�y wi�h C�����a�� E���p��<br />
�G����a�y 66��1 %� is as hi�h as �ha� �f �h�� �i���c�<br />
���i�h��� �����ia & ������������ �64��2%�. Th�� ���w��s�<br />
si�i��a�i�i��s hav�� ������ f���� wi�h �h�� c�����a�� a��<br />
w��s����� ����i�����a���a� ����i�� ���p���s������� �y<br />
I�a��y �47��9 %� a�� �h�� I����ia� P���i�s���a �36��9 %�.<br />
Acknowledgements<br />
The first author would like to thank Peter J. Neu<br />
a�� �h�� ��s��� �a�i��a�� ��his��i��� �a�������������<br />
������������� f�� �h��i� s�pp��� �� pa��icipa��� i�<br />
�h�� sy�p�si��.<br />
References<br />
Barnard P. (ed.) 2005. - <strong>Trichoptera</strong>. Caddisflies.<br />
Fauna Europaea version ersion 1.2; http://www.<br />
fa��a����.���.<br />
B��a �. 1943-4�. - E�����yi ��������s��� va�y<br />
szőrősszárnyúak (<strong>Trichoptera</strong>). Múzeumi<br />
Füzetek 3: 1-4.<br />
B���sa���a�� �. 19�2 . - C����i���ii ��a s���i��� �����v���tarii<br />
postembrionare si biologiei trichopterelor:<br />
Rhyac�phi��a ��a��vis Pic�. �Rhyac�phi��i�a����� �Rhyac�phi��i�a����� �yp�� �yp��<br />
pha���pa ����ph. �Psych��yi�a����� Ecc��is�p����y�<br />
guttulata Pict. (Ecclisopteryginae), Lithax niger<br />
Hag. (Goerinae). Buletin Stiintific Sectiunea<br />
��� ��ii���� Bi�����i���� �������i���� G�������ic�� si<br />
Geografice 4(4): 895-932.<br />
Table 3: Comparison of the Romanian <strong>Trichoptera</strong> fauna with other selected European states by the<br />
use of Bray-Curtis index of similarity based on presence/absence data. The number of species<br />
is corrected after Malicky (2005).<br />
State<br />
Bray-Curtis<br />
index in %<br />
Number of<br />
species<br />
Number of<br />
species in<br />
common<br />
Reference<br />
����va�ia 77��2 216 186 Ba��a�� �200��<br />
P���a�� 72��6 288 201 C��ach���ws�i �200��<br />
H���a�y 72��0 209 171 N���a�i & Uh�����vich �2002�<br />
B����a�ia 69��9 246 179 Ba��a�� �200��<br />
G����a�y 66��1 31� 192 R������ �2004� & a��i���s<br />
�����ia &<br />
64��2 201 1�0 Ba��a�� �200��<br />
������������<br />
G�����c�� �4��3 246 139 Ba��a�� �200��<br />
N��way �1��0 193 117 J�ha��s�� �2003�<br />
I�a��y 47��9 389 1�7 Cianficconi (2002) & additons<br />
I����ia� P���i�s���a 36��9 3�2 114 Wi�����-�a�s��� �2004�<br />
R��a�ia 266<br />
<strong>Ferrantia</strong> • 55 / 2008
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Botosaneanu L. 1973. - Les Trichopteres (Insecta:<br />
T�ich�p����a� ��� �����spac�� ���spac�� ��spac�� Ca�pa��-Ba��ca�iq�����<br />
Ca�pa��-Ba��ca�iq�����<br />
Ca�pa��-Ba��ca�iq�����<br />
f����iss����s ��� ��c��������s p��� ��������� ������� ������ ��� ��� ���<br />
l�evolution. �evolution. evolution. Rivista di Idrobiologia 12 (2/3):<br />
119-1�2.<br />
B���sa���a�� �. 197�. - Di�� �������isch��� T�ich�p-<br />
������� ���� Ka�pa����. V���ha���������� ���s<br />
���chs���� I������a�i��a����� �y�p�si��s ü����<br />
Entomofaunistik in Mitteleuropa: 91-103.<br />
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f��� R��a�ia a�� s��v���a�� sp��ci��s ���w �� �h��<br />
c�����y�s �ss fa��a fa��a fa��a �T�ich�p����a�. �T�ich�p����a�. �T�ich�p����a�. E���������isch��<br />
E���������isch��<br />
E���������isch��<br />
Zeitschrift 103 (21): 399-404.<br />
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�h�� ���w�������� �f �h�� T�ich�p����a �f R��a�ia��<br />
wi�h �a�a �� E���p��a� �a�a f��� ���si��� �his<br />
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����.��� P��c�����i��s �f �h�� 10 �h I������a�i��a��<br />
�y�p�si�� �� T�ich�p����a. N�va ��pp���������a<br />
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�iv����� Ci������� �����ai�s�� ����h Ca�pa�hia�s��<br />
Romania: 343-348, in Mey W. (ed.), Proceedings<br />
�f �h�� 10 �h I������a�i��a�� �y�p�si�� ��<br />
T�ich�p����a. N�va ��pp���������a E���������ica<br />
1��� G���c��� & Ev���s�� K���������.<br />
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�I�s��c�a�. T�ava�� �� ��s���� ��His��i��� �His��i��� His��i���<br />
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���s ����i�����a�����i�����s. . �i������ �i������ �i�����isch��<br />
�i�����isch��<br />
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R����i H���a�ia���� pp. 33-41�� B��ap��s�.<br />
�����ci �. & �a�c�ci-��������sc� �. 19��. - C����i-<br />
���ii ��a c���as������a ��ich�p���������� �i� Ba��i����<br />
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��������s��i �T�ich�p����a�. D��á��ú��i D�������a���<br />
(A) Természettudomaányi Sorozat 11:1-386.<br />
P����ác�� �. 1914. - �a�ya���s��á� N�����p�����i�ái.<br />
E������a�i� N�����p�����i��� R����i H���a�ia��.<br />
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V�������ich�is �i� V�������i����sa��a����. �. 107-<br />
151 in: Klausnitzer, B. (Hrsg.): Entomofauna<br />
G����a�ica �. E���������isch�� Nach�ich����<br />
und Berichte, Beiheft 6; Dresden.<br />
R������ B. 2004. - �ys����a�isch��s V�������ich�is ����<br />
Köcherfliegen (<strong>Trichoptera</strong>) Deutschlands.<br />
Fortschreibung 02/2004. – Entomologie heute<br />
16: 93-107.<br />
R������ �.C. & C�����a�-Ba�a��c �. 200�. - �sp��c�s<br />
c��c����i�� Ta��ava �a��� a�� Ta��ava �ica<br />
rivers (Transylvania, Romania) caddisfly<br />
123
L. Ujvárosi árosi rosi et et al. First revision of the Romanian caddisflies<br />
124<br />
�I�s��c�a. T�ich�p����a� ��a�va�� c�����i�i��s��<br />
in: Curtean-Banaduc A., Banaduc D. & Sirbu<br />
I. ����s.��� Th�� Ta��ava Riv��� Basi��� T�a�sy��va�ia�<br />
R��vi��w �f �ys����a�ica�� a�� Ec�����ica��<br />
Research 2: 89-97.<br />
Ujv�si �. 1994. - C����i���ii ��a c���as������a<br />
faunistica a trichopterelor (Insecta: <strong>Trichoptera</strong>)<br />
�i� D��p���si����a Ci�c. B������i� ��� i�f���a���<br />
- Societatea Lepidopterologica Romana 5 (2):<br />
149-163.<br />
Ujv�si �. 199�. - D��a sp��cii ��i si ca���va sp��cii<br />
�a��� ��� ��ich�p������ p������ fa��a R��a�i��i.<br />
B������i� ��� i�f���a��� - ��ci���a���a ���pi��p�����logica<br />
Romana 6 (1-2): 151-155.<br />
Ujv�si �. 1997a. - Fa��a ��� ��ich�p������ �i�<br />
Masivul Retezat si Valea Cernei (Insecta:<br />
<strong>Trichoptera</strong>): 75-86, in Rákosy L. (ed.), Entomofa��a<br />
pa�c��i���� �a�i��a���� R�������a� si Va����a<br />
C������i.<br />
Ujv�si �. 1997�. - ����y �� �h�� T�ich�p����a<br />
fa��a i� �h�� R��a�ia� s��c�i�� �f �h�� Riv���<br />
Crisul Alb catchment area: 295-299, in<br />
�á��á�y-Kiss �. & Ha�a� J. ����s��� Th��<br />
Criş/Körös Rivers� Valleys. A study of the<br />
������aphy�� hy����i�����y a�� ��c�����y �f �h��<br />
�iv��� a�� i�s ���vi��������. Tiscia ������aph<br />
s���i��s�� Tis��a K���� & �i�a P�� E���pa�� ���������<br />
- Szeged - Tîrgu Mureş.<br />
Ujvárosi L. 1997c. - <strong>Trichoptera</strong>, in: Rákosy L. (ed.),<br />
R��������a������� �a������i �����������ic�� �i� Ch��i����<br />
Tisi���i�� ����ii V�a�c��i�� B������i� ��� i�f���a���<br />
- Societatea Lepidopterologica Romana 8(1-2):<br />
11-14.<br />
Ujvárosi L. 1998a. - Trichopterele (Insecta:<br />
T�ich�p����a� �i� ����a Ch��i���� �����s����i Ca���<br />
�Ic P�����. B������i� ��� i�f���a��� - ��ci���a���a<br />
Lepidopterologica Romana 9(3-4): 265-268.<br />
Ujv�si �. 1998�. - F��� T�ich�p����a sp��ci��s<br />
���w i� �h�� R��a�ia� fa��a. E���������ica<br />
Romanica 3: 73-78.<br />
Ujv�si �. 1999. - C����i���ii ��a c���as������a<br />
fa��is�ica a ��ich�p���������� �I�s��c�a�� T�ich�p����a�<br />
�i� G��pa C�����a��a a Ca�pa�i���� O�i����a��i.<br />
��a�������� U�iv���si�a�ii �i� O�a���a�� Fascic���a<br />
Biologie 4: 49-87.<br />
Ujvárosi L. 2000. - Angaben über die Köcherfliegen<br />
�T�ich�p����a� ���s �aci� G���i����s�� i� R�sy<br />
�. & Wi��s��� C. ����s.��� Das �aci� G���i����<br />
�R��ä�i����� N���-D�����scha��� Ca�i��hia II<br />
190/110:110.<br />
Ujv�si �. 2002a. - Th�� p���s���� s�a��� �f �h��<br />
���w�������� �� �h�� T�ich�p����a �f �h�� c�����a��<br />
group of the Eastern Carpathians in Romania:<br />
379-394�� i� ���y W. ����.��� P��c�����i��s �f �h��<br />
10 �h I������a�i��a�� �y�p�si�� �� T�ich�p����a.<br />
N�va ��pp���������a E���������ica 1��� G���c���<br />
& Ev���s�� K���������.<br />
Ujv�si �. 2002�. - Th�� p���s���� s�a��s �f �h���a�<br />
to the caddisflies (<strong>Trichoptera</strong>) from the rivers<br />
�����s�� �����s a�� C�is��i ca�ch����� a���a i�<br />
Romania. Tiscia monograph series 6:149-165.<br />
Ujvá��si �. 2003. - E�y��s �������yi ���yi f���yós��a�as����<br />
f���yós��a�as����<br />
minősítése és osztályozása jellegzetes tegzesegyütteseik<br />
(<strong>Trichoptera</strong>) alapján: 152-215, in<br />
Ujvá��si �. ����.��� E�����y F���yói�a� ������s�����i<br />
á����ap��a. �api����ia Kö�yv��� 21�� �ci����ia Kia�ó��<br />
C���j-Nap�ca.<br />
Ujv�si �. & Chis� �.C. 1999. - C����i���i�� ��<br />
the knowledge of the caddisflies (Insecta:<br />
<strong>Trichoptera</strong>) fauna of the Olt River Basin. in:<br />
�i��� I.�� C�����a� �. & Ba�a��c D. ����s.��� Th��<br />
Upp��� a�� �i������ O��� Riv��� Basi��� T�a�sy��va�ia�<br />
R��vi��w �f �ys����a�ica�� a�� Ec�����ica��<br />
Research 1: 129-142.<br />
Ujv�si �. & N����� G. 1996. - Da��� as�p�a<br />
speciilor de trichoptere (Insecta: <strong>Trichoptera</strong>) si<br />
a��������a ���� �����a�iv�� i� ����a Vi��a �Ca�pia<br />
R��a�a�. B������i� ��� i�f���a��� - ��ci���a���a<br />
Lepidopterologica Romana 7 (1-2): 139-144.<br />
Ujv�si �. & N���a�i �. 1999. - Th�� f���a���� �f<br />
P��a��phy��a� j���i ���y�� 1976 �T�ich�p����a��<br />
Limnephilidae). Braueria 26: 24.<br />
Ujv�si �.�� N���a�i �. & Uh�����vich �. 199�. -<br />
����i��s �� �h�� T�ich�p����a fa��a �f �h�� Ci�c<br />
Basi� a�� Ha��hi�a �����ai�s�� R��a�ia. F���ia<br />
Historico Naturalia Musei Matraensis 20: 99-<br />
113.<br />
Wiberg-Larsen P. 2004. - Danish <strong>Trichoptera</strong>–<br />
sp��ci��s �iv���si�y�� �i�����ica�� ��ai�s�� a�� a�����<br />
�isp���sa��. 220pp.�� Ph.D.-�h��sis�� F���shwa����<br />
Bi�����ica�� �a���a���y�� Fac����y �f �ci���c����<br />
U�iv���si�y �f C�p���ha���� & Fy� C����y�� D��p�.<br />
Na����� & �q�a�ic E�vi���������� C�p���ha����.<br />
Wiggins G. B. 1998. - The caddisfly family Phryga-<br />
���i�a�� �T�ich�p����a�. U�iv���si�y �f T������<br />
P���ss�� T�������� 306 p.<br />
<strong>Ferrantia</strong> • 55 / 2008
G. Urbanič Zoogeographic division of Slovenia based on caddisfly distribution<br />
Zoogeographic division of Slovenia based on<br />
caddisfly distribution<br />
Abstract<br />
Distribution of caddisflies, collected at more than 800<br />
si���s�� was �s��� �� �a��� a ����������aphic �ivisi�� �f<br />
����v���ia. F��� �a���a�� ������aphic ��i�s - ���ps�� Di�a�i�s��<br />
Pa����ia� ���w��a�� a�� P� ���w��a�� - w����� s������c����<br />
a p�i��i as ����������aphic ����i��s. Th�� ����h�� �f<br />
����������aphic i��ica�iv�� sp��ci��s �sp��ci��s �cc���i��<br />
i� ����y ���� ����i�� acc���i�� �� �h�� ��i����a����� �a�a a��<br />
�is��i���i�� i� ����v���ia� was �s��� f�� a�����ca�i�� �f<br />
sa�p��i�� si���s �� ���� �f �h�� ����i��s. This ����h�� was<br />
Introduction<br />
���v���a�� ����������aphic �ivisi��s �f ����v���ia w�����<br />
made in the past (Carnelutti 1992; Hadži 1931;<br />
Illies 1978; Mršić1997; Sket 2003). They were made<br />
��i�h��� f�� �h�� a���a �f ����v���ia ����y �� ����v���ia<br />
was i�c������� as a pa�� �f a ��a����� ������aphic<br />
area (e.g. former �ugoslavia (Hadži 1931), Europe<br />
�I����i��s 1978���� which i�pac���� a��s� �h�� p���cisi��<br />
�f �����i���a�i�� �f �h�� ����i��s. F���h���������� �h��s��<br />
�ivisi��s w����� �a��� �si�� �a�a �� �is��i���i�� �f<br />
i) terrestrial animals (e.g. Carnelutti 1992; Mršić<br />
1997; ����� 2003��� ii� �������s��ia�� a�� f���shwa����<br />
animals (Hadži 1931; Sket 2003) or iii) only<br />
f���shwa���� a�i�a��s �I����i��s 1978; ����� 2003�.<br />
Results of these divisions proved that different<br />
groups of organisms have different distribution<br />
patterns. Banarescu (1972) stated that only among<br />
f���shwa���� a�i�a��s f��� �ai� �yp��s �f �is��i���i��<br />
ca� ��� acc��p���� c��si����i�� �is��i���i��s �f si������<br />
sp��ci��s a�� ��� ��i���a���s. Th��s�� a��� �is��i���i�� �f<br />
i� ��pi�a��a� p�i�a�y aq�a�ic a�i�a��s ii� hyp����a�<br />
f���shwa���� a�i�a��s iii� p�i�a�y aq�a�ic a�i�a��s a��<br />
iv� aq�a�ic i�s��c�s. I� ����v���ia�� �ivisi��s �as��� ��<br />
f���shwa���� a�i�a��s w����� p���f������ �� hyp����a�<br />
f���shwa���� a�i�a��s ������ 2003��� ��pi�a��a� p�i�a�y<br />
aq�a�ic a�i�a��s ������ 2003��� p�i�a�y aq�a�ic<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Gorazd Urbanič<br />
D��pa������� �f Bi�����y�� Bi����ch�ica�� Fac����y<br />
U�iv���si�y �f �j����ja�a<br />
Večna pot 111,<br />
�I-1000 �j����ja�a�� ����v���ia<br />
���a���.���a�ic@�f.��i-��j.si<br />
f������w��� �y �������ic �����i�i����si��a�� sca��i�� �N���<br />
of sampling sites containing at least five species. NMS<br />
method confirmed that sites of each of the selected four<br />
����i��s a��� ����p��� ������h���. This ����h�� was a��s� �s���<br />
f�� a�����ca�i�� �h�� sa�p��i�� si���s wh����� �� i��ica�iv��<br />
sp��ci��s w����� f����. I� a��i�i�� �� f��� ����i��s�� �w�<br />
s������i��s i� �h�� ���pi��� ����i�� a�� Di�a�ic ����i����<br />
���sp��c�iv����y�� w����� ��������i����.<br />
a�i�a��s ������ 2003� a�� a��s� aq�a�ic i�s��c�s �I����i��s<br />
1978). However, the latter one was performed as<br />
a pa�� �f a ����������aphic �ivisi�� �f E���p�� ��<br />
the scale 1:24 million and in the case of Slovenia<br />
a��s� p���i�ica�� �������s w����� �s��� f�� �����i���a�i�� �f<br />
����i��s. ������v����� ����� �f �h��s�� �ivisi��s w�����<br />
s�pp������ �y s�a�is�ica�� a�a��ys��s.<br />
Th�� ai� �f �his w��� was �� �a��� a ����������aphic<br />
division of Slovenia based on the caddisfly<br />
�is��i���i�� a�� s�pp��� �his �ivisi�� �y s�a�is�ica��<br />
a�a��ysis.<br />
Material and methods<br />
O�� ����������aphic a�a��ysis was �as��� ��<br />
caddisflies - adults and larvae collected at 804<br />
����i�� wa���� sa�p��i�� si���s a���� �v��� ����v���ia<br />
�Fi�. 1�. ��s� �f �h�� �a����ia�� was c�������c���� �y<br />
���s��a�ch���s �f �h�� ����v���ia� ��s���� �f Na���a��<br />
His���y�� Bi����ch�ica�� Fac����y D��pa������� �f<br />
Bi�����y a�� E�vi��������a�� �����cy �f �h�� R��p����ic<br />
�f ����v���ia ����w����� 198� a�� 2003�� a���h���h s����<br />
������� sa�p����s w����� a��s� c��si�������. I� s�a�is�ica��<br />
a�a��ys��s ����y sp��ci��s �a�a w����� �s���. ����� sp��ci��s<br />
collected at one sampling site possibly at different<br />
�a���s ���p���s������� a� �p���a�i��a�� ��i� �OU���<br />
which was �s��� i� �h�� a�a��ys��s as a s�a�is�ica��<br />
125
G. Urbanič Zoogeographic division of Slovenia based on caddisfly distribution<br />
126<br />
Fig. 1: Map of the sampling sites and the river network of Slovenia.<br />
sa�p����. �p��ci��s c�������c���� �si�� ��i�h� ��aps w�����<br />
not considered because of the possible attraction<br />
of caddisflies from long distances (Malicky 1987,<br />
Urbanič 2003).<br />
Steps in the zoogeographic analyses<br />
1. In a first step four main regions were a priori<br />
��������i���� acc���i�� �� �h�� ���c���ic �ap �f<br />
����v���ia a�� ���i�h����i�� ����i��s �Fi�.2�. Th��s��<br />
����i��s a��� ���ps �� �h�� ����h�� Di�a�i�s �� �h��<br />
s���h�� Pa����ia� ���w��a�� �� �h�� ��as� a�� P�<br />
���w��a�� �� �h�� w��s� �f ����v���ia.<br />
2. D�������i�a�i�� �f �h�� i��ica��� sp��ci��s.<br />
a) First, the first class indicator species were<br />
��������i����. ��ch w����� c��si������� a���� sp��ci��s<br />
which w����� f���� ����y i� ���� �f �h�� a p�i��i<br />
��������i���� ����i��s acc���i�� �� ��i����a�����. �i���s<br />
containing first class indicator species were<br />
allocated to the region that the first class indicator<br />
sp��ci��s ���p���s�������. �pp��p�ia������ss �f s�ch a<br />
priori classification was tested using a nonmetric<br />
�����i�i����si��a�� sca��i�� �N��� a�a��ys��s. �i���s<br />
containing at least five species were included in<br />
�h�� a�a��ys��s.<br />
�� I� �h�� ����� s���p s��c��� c��ass i��ica��� sp��ci��s<br />
- sp��ci��s �ha� �cc�� i� �w� �f �h�� f��� a p�i��i<br />
��������i���� ����i��s w����� ��������i���� ���.�. i� �h��<br />
���ps a�� Di�a�i�s�. F�� si��� a�����ca�i�� ���c���si��<br />
p�i�cip���� was �s���; if a� �h�� sa��� sa�p��i�� si���<br />
a sp��ci��s �cc�������� �ha� is f���� i� ���ps a��<br />
Di�a�i�s a�� a���h��� sp��ci��s�� f���� i� Di�a�i�s<br />
a�� Pa����ia� ���w��a���� �h�� si��� was a�����ca���� ��<br />
�h�� Di�a�ic ����i��. �pp��p�ia������ss �f s�ch a p�i��i<br />
classification was tested again using a nonmetric<br />
�����i�i����si��a�� sca��i�� �N��� a�a��ys��s. O���y<br />
sites containing at least five species were included<br />
i� �h�� a�a��ys��s.<br />
c� Th�� p��c������� �f �h�� a�����ca�i�� �f si���s c���ai�i��<br />
first and second class indicator species was used<br />
a��s� f�� �h�s�� si���s which w����� ��� i�c������� i� �h��<br />
N�� a�a��ys��s ���ca�s�� �h�� ������� �f sp��ci��s was<br />
��� ���w.<br />
<strong>Ferrantia</strong> • 55 / 2008
G. Urbanič Zoogeographic division of Slovenia based on caddisfly distribution<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Fig. 2: Very simplified synthetical structure tectonic map of central and western Balkan and<br />
adjacent regions (a – Outer Dinarids and Helenids, b – Inner Dinarids and Helenids, c – Southern<br />
Alps, d – Eastern Alps, e – deep sea sediments, f – young tectonic hollows filled with Molasse, g<br />
– remains of the oceanic lithosphere (ophiolits), h – a tectonically affected edge of the Eurasian<br />
plate, i – a stable Eurasian plate) (Mršić, 1997: 38).<br />
3. �i���s �ha� c���ai���� s��c��� c��ass i��ica���<br />
sp��ci��s ��� wh����� ���c���si�� p�i�cip���� c����� ��� ���<br />
�s����� ���ca�s�� ����y sp��ci��s cha�ac����is�ic f�� �w�<br />
����i��s w����� p���s������ w����� a�a��ys��� ������h��� wi�h<br />
a���� si���s a�����ca���� �� ���� �f �his �w� ����i��s �si��<br />
a N�� a�a��ysis. Th��s�� si���s w����� a�����ca���� i� ����<br />
�f �h�� �w� ����i��s acc���i�� �� �h�� ass������a���<br />
si�i��a�i�y.<br />
4. �a�p��i�� si���s wh����� �� i��ica��� sp��ci��s w�����<br />
c�������c���� �����ss �ha� � % �f a���� si���s� w����� a�����ca����<br />
�� ���� ����i�� acc���i�� �� �h��i� ������aphic<br />
p�si�i��.<br />
5. For final delineation of regions all sampling<br />
si���s �f �w� ���i�h����i�� ����i��s w����� a�a��ys���<br />
a�ai� �si�� N�� a�a��ys��s ���.�. ���pi��� ����i�� a��<br />
Di�a�ic ����i���� ��� ��� Pa����ia� ����i�� a�� P�<br />
����i���.<br />
B��si��� �h�� p��c������� f�� �����i���a�i�� �f ����i��s<br />
a��s� a p��c������� f�� �����i���a�i�� �f �w� s������i��s<br />
i� ���ps a�� Di�a�i�s was p���f������. I� ���h cas��s<br />
�h�� sa��� p��c������� was �s���.<br />
Results<br />
Delineation of regions<br />
On the basis of the indicator caddisfly species<br />
�is��i���i�� a�� �h�� si�i��a�i�y a�a��ys��s �f<br />
sp��ci��s ass������a���s�� a �����i���a�i�� �f f���<br />
hy�������������aphic ����i��s was �a��� i� ����v���ia<br />
(Fig. 3):<br />
- ���pi��� ����i��<br />
- Di�a�ic ����i��<br />
- Pa����ia� ����i�� a��<br />
- P� ����i��.<br />
Th�� ���pi��� ����i�� i�c������s wa����c���s��s �f ����h-<br />
��as����� a�� ��as����� ����v���ia. I� �h�� Di�a�ic ����i��<br />
127
G. Urbanič Zoogeographic division of Slovenia based on caddisfly distribution<br />
128<br />
Fig. 3: Hydrozoogeographic regions and subregions (ZA – West alpine, VA – East alpine, ED – Eudinaric, SD – Submediterranean-dinaric)<br />
of Slovenia according to distribution of caddisflies; points represent sampling sites.<br />
��s� wa����c���s��s �f �h�� s���h���� ����v���ia a��<br />
p��ai�s �f �h�� c�����a�� ����v���ia w����� i�c�������.<br />
Wa����c���s��s �f ���w��a��s a�� hi����y ����i�� �f<br />
s���h-��as����� a�� ��as����� ����v���ia c��p�s�� �h��<br />
Pa����ia� ����i���� wh�����as �h�� P� ����i�� i�c������s<br />
wa����c���s��s �f �h�� s�a������� pa�� �f �h�� ���w��a��<br />
a�� hi����y ����i�� �f w��s����� ����v���ia. ���pi���<br />
a�� Di�a�ic ����i��s w����� ��ach �ivi���� i��� �w�<br />
subregions. The Alpine region was divided into:<br />
- W��s� a��pi��� s������i��; �his s������i�� i�c������s<br />
wa����c���s��s �f �h�� w��s� a�� c�����a�� ���pi���<br />
����i���� wi�h ��s���y ca����a��� ��������y.<br />
- Eas� a��pi��� s������i��; �his s������i�� i�c������s<br />
wa����c���s��s �f �h�� ��as� ���pi��� ����i���� wi�h<br />
��s���y si��ica��� ��������y.<br />
Dinaric region was divided into:<br />
- �������i�����a���a�-�i�a�ic s������i��; �his<br />
s������i�� i�c������s wa����c���s��s �f �h�� s���hw��s�<br />
dinaric region with mostly flysch geology. All<br />
�h��s�� wa����c���s��s�� apa�� �f �h�� Piv�a �iv���<br />
�asi��� a��� pa�� �f �h�� ���ia�ic �iv��� �asi�.<br />
- E��i�a�ic s������i��; �his s������i�� i�c������s<br />
wa����c���s��s �f �h�� c�����a�� a�� ��as� Di�a�ic<br />
����i���� wi�h ��s���y ca����a��� ��������y. �����<br />
�h��s�� wa����c���s��s a��� pa�� �f �h�� Da����� �iv���<br />
�asi�.<br />
Statistical analyses<br />
� ���a�� �f 237 sp��ci��s w����� ��������i���� a�� �s���<br />
in the similarity analyses of the caddisfly species<br />
ass������a���s. Of �h�� ��������i���� sp��ci��s�� 89 w�����<br />
f���� ����y i� ���� ����i��. Th�� ��s� sp��ci��s w�����<br />
f���� i� �h�� ���pi��� ����i��. �a�y sp��ci��s �f �h��<br />
s��fa�i��y D��si�a�� ���.�. Drusus destitutus�� D.<br />
monticola�� D. slovenicus�� Ecclisopteryx asterix�� E.<br />
guttulata…), some Rhyacophila sp��ci��s ���.�. R.<br />
stigmatica�� R. bonaparti�� R. glareosa…), Tinodes<br />
sp��ci��s ���.�. T. zelleri�� T. sylvia� a�� s���� ��h���<br />
sp��ci��s �cc�� ����y i� �h�� ���ps. ����� ������h����� �3<br />
sp��ci��s w����� f���� ����y i� �h�� ���pi��� ����i��. I�<br />
�h�� Di�a�ic ����i���� 27 sp��ci��s w����� f����. �����<br />
D��si�a�� sp��ci��s ���.�. Ecclisopteryx dalecarlica��<br />
<strong>Ferrantia</strong> • 55 / 2008
G. Urbanič Zoogeographic division of Slovenia based on caddisfly distribution<br />
Drusus croaticus��� Rhyacophila sp��ci��s ���.�. R.<br />
palmeni� a�� Chaetopteryx sp��ci��s �C. irenae�� C.<br />
marinkovicae� a��� �h�� ��s� cha�ac����is�ic. 18<br />
sp��ci��s w����� f���� ����y i� �h�� Pa����ia� ����i����<br />
a�� sp��ci��s �f �h�� fa�i��y ���p��c���i�a�� ���.�.<br />
Triaenodes bicolor�� Ceraclea riparia� w����� �h�� ��s�<br />
cha�ac����is�ic. I� �h�� P� ����i�� ����y Tinodes antonioi<br />
was a cha�ac����is�ic sp��ci��s.<br />
Results of the NMS analyses confirmed the correct<br />
a p�i��i a�����ca�i�� �f �h�� sa�p��i�� si���s �� f���<br />
����i��s ����pi����� Di�a�ic�� Pa����ia��� P�� acc���i��<br />
�� �h�� �cc������c�� �f �h�� i��ica��� sp��ci��s �Fi�s.<br />
4-5). Similarity analyses showed that caddisfly<br />
ass������a���s i� �h�� ���pi��� ����i�� a�� Pa����ia�<br />
����i�� a��� �h�� ��s� �iv���s��. P�i��s �ha� �a�� �h��s��<br />
sa�p��i�� si���s a��� �� �h�� �pp�si��� si���s �f �h��<br />
���i�a�i�� �ia��a�. B���w����� �h��s�� �w� ����i��s<br />
a��� p�i��s �ha� �a�� sa�p��i�� si���s �f �h�� Di�a�ic<br />
����i��. P�i��s �ha� �a�� sa�p��i�� si���s �f �h��<br />
P� ����i�� a��� ���ca���� ������h��� wi�h p�i��s �f �h��<br />
Pa����ia� ����i���� which ���a�s �ha� i� ���h �h��s��<br />
two regions similar caddisfly species assemblages<br />
w����� f����.<br />
NMS2<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
NMS1<br />
Discussion<br />
Zoogeographic regions<br />
G�����aphic p�si�i�� �f ����v���ia�� wh�����<br />
�����ai���s ���ps a�� Di�a�i�s ������ a�� wh�����<br />
�h����� a��� c���i�����a�� a�� ����i�����a���a� ���w��a��s<br />
���s������� ��� ����y i� �h�� hi�h �i��iv���si�y �f �h��<br />
a���a�� ��� a��s� i� �h�� �v�����appi�� �f �is��i���i��<br />
areas of species characteristic of different<br />
����������aphic ��i�s. �s a c��s��q����c���� �his �i�<br />
of fauna constrained many different approaches<br />
a�� ���s����s �f �h�� ����������aphic �ivisi��s. �����<br />
�2003� a��s� �a���� s���� ����i��s as a c���i�a�i��<br />
�f �w� ������aphic ����i��s ���.�. ���pa����ia�p����i�a�ic<br />
����i���.<br />
F��� app��ach��s �f ����������aphic �ivisi�� �f<br />
����v���ia w����� �as��� �� f���shwa���� a�i�a��s �I����i��s<br />
1978�� ����� 2003��� ��� ����y �ivisi�� �f I����i��s �1978�<br />
i�c������� �h���phi��ic aq�a�ic i�s��c�s. H�w��v�����<br />
latter division was performed on a large scale<br />
a�� ����v���ia c����i������ �� �w� ����������aphic<br />
���c������i��s ����y�� ���ps ���c�����i�� 4� a�� W��s�����<br />
Di�a�ic Ba���a� ���c�����i�� ���� a���h���h ����v���ia<br />
���������� a��s� �� �w� ����� ���i�h����i�� ����i��s��<br />
Fig. 4: Nonmetric multidimensional scaling ordination diagram of sampling sites containing at least one indicator<br />
species, the overlay indicates the hydrozoogeographic region: AL – Alpine region, DN – Dinaric region, PN – Pannonian<br />
region, PA – Po region. Stress = 0,15.<br />
PN<br />
DN<br />
AL<br />
PA<br />
129
G. Urbanič Zoogeographic division of Slovenia based on caddisfly distribution<br />
NMS2<br />
H���a�ia� ���w��a�� ���c�����i�� 11� a�� I�a��y<br />
���c�����i�� 3�. I� ��� s���y w�� a�����ca��� ��a����<br />
��as����� pa�� �f ����v���ia� a���a �� Pa����ia�<br />
���w��a���� wha� �i�h� c�����sp��� �� I����i��s��<br />
��c�����i�� H���a�ia� ���w��a��. H�w��v����� �� �h��<br />
w��s� I����i��s �1978� ��������i���� Ec�����i�� I�a��y��<br />
which i�c������s a��s� ���ps �� �h�� ������va�i�� �f 1000<br />
�. I� �h�� w��s� �f ����v���ia ��� app��ach ����s ���<br />
fit the Illies� � one. ����. ����. Only O���y O���y small s�a���� s�a���� hilly hi����y hi����y and a�� a�� lowland ���w��a�� ���w��a��<br />
a���a �p �� 200 � was ���c���is��� as �h�� P� ����i��.<br />
Also in central Slovenia different approaches were<br />
used. It is obvious that here we can find Alpine<br />
a�� Di�a�ic sp��ci��s a�� �ha� �����i���a�i�� �f �h��<br />
area is not simple (Sket 2003, Urbanič 2004). This<br />
might be also the reason why Illies (1978) defined<br />
�h�� ������� ����w����� �h�� ��c�����i�� 4 ����ps� a��<br />
��c�����i�� � �Di�a�ic W��s����� Ba���a�� v���y si�p��y.<br />
Dispersal ability of caddisflies is the reason why<br />
geographic division (Perko & Orožem Adamič<br />
1998� �f �h�� Di�a�i�s a�� ���ps �as��� �ai���y ��<br />
his���ica�� ��v����s ����s ��� c�����sp��� w������ �� ���<br />
�ivisi��. I� �h�� s� ca������� "���pi��� "���pi��� ���pi��� p��ai�s" p��ai�s" p��ai�s" " �f �f �f �f �f �h�� �h�� �h�� �h�� �h��<br />
c�����a�� ����v���ia �i�a�ic sp��ci��s ca� ��� f���� ���.�.<br />
Rhyacophila schmidinarica�� R. palmeni�. ������v�����<br />
130<br />
NMS1<br />
Fig. 5: Nonmetric multidimensional scaling ordination diagram of all sampling sites, the overlay indicates the<br />
hydrozoogeographic region: AL – Alpine region, DN – Dinaric region, PN – Pannonian region, PA – Po region. Stress<br />
= 0,15.<br />
PN<br />
DN<br />
AL<br />
PA<br />
i� �h�� ����w��s����� pa�� �f �h�� Di�a�ic �����ai�s<br />
(Idrijsko hribovje) typical alpine species can be<br />
f���� ���.�. Ecclisopteryx asterix�� Metanoea rhaetica�.<br />
On the other hand, at the prealpine lake outflows<br />
no typical alpine caddisfly species were found.<br />
Moreover, at the Bohinj lake outflow Micrasema<br />
setiferum was f������ a sp��ci��s which �cc��s<br />
i� ����v���ia ����y i� �h�� Di�a�ic ����i�� wi�h a<br />
p���a���y �isj��c�iv�� a���a a� �h�� B�hi�j ��a���<br />
outlet (Urbanič 2004). Also the whole caddisfly<br />
ass������a��� f���� a� �his ��a��� �������� was �����<br />
si�i��a� �� ass������a���s f��� �h�� Di�a�ic ����i��<br />
�ha� �� ���pi��� ����i��. Th�� ���as�� is p���a���y i�<br />
�h�� hi�h s������ ����p���a�����s which i�pac� �h��<br />
caddisfly distribution most (Urbanič 2004). The<br />
i�p���a�c�� �f �h�� s������ �a�i��� ����p���a�����<br />
on caddisfly distribution was obvious also at<br />
�a�s� sp�i��s wh����� a� ���w ������va�i�� �ypica��<br />
�����ai���s sp��ci��s w����� f������ which ���s�������<br />
i� s���� is��a��s a�� �aps �f ���� ����i�� i�si���<br />
a���h���. Th�� ��h��� ���as�� f�� s�ch �aps is a��s�<br />
a flow of a large plain river with caddisflies<br />
cha�ac����is�ic f�� ���w��a�� �iv���s �h����h �h��<br />
is���a���� a��pi��� �����ai� �a����. ��ch cas��s a���<br />
<strong>Ferrantia</strong> • 55 / 2008
G. Urbanič Zoogeographic division of Slovenia based on caddisfly distribution<br />
NMS2<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
NMS1<br />
Fig. 6: Nonmetric multidimensional scaling ordination diagram of sampling sites of the Alpine region, the overlay<br />
indicates the hydrozoogeographic subregion: VA – Eastalpine subregion, ZA – Westalpine subregion. Stress = 0,17.<br />
NMS2<br />
NMS1<br />
Fig. 7: Nonmetric multidimensional scaling ordination diagram of sampling sites of the Dinaric region, the overlay<br />
indicates the hydrozoogeographic subregion: ED – Eudinaric subregion, SD – Submediterranean-dinaric subregion.<br />
Stress = 0,18.<br />
ED<br />
SD<br />
VA<br />
ZA<br />
131
G. Urbanič Zoogeographic division of Slovenia based on caddisfly distribution<br />
132<br />
�ava Riv��� a�� �avi�ja Riv��� �h����h P�savs��<br />
hribovje and Drava River which flows between<br />
P�h��j�� a�� K���ja�. Gaps �f �h�� ���pi��� ����i��<br />
i�si��� �h�� Di�a�ic ����i��s ca� ��� f���� a��s� a� �h��<br />
p��ai�s wh����� ��a���� �iv��� ����av�� �h�� �����ai�s a��<br />
������� �h�� p��a���. I� ���h cas��s �f �aps�� �h�� p���s���c��<br />
of alpine elements in the first case and Pannonian<br />
in the latter also confirms the theory that the water<br />
����p���a����� �a�i��� is a� i�p���a�� ��c�����ica��<br />
factor affecting the caddisfly distribution in the<br />
Alps and Dinarids (Urbanič 2004).<br />
Statistical analyses<br />
Usi�� a� i��ica��� sp��ci��s app��ach a�� N��<br />
analyses, we confirmed the a priori determination<br />
�f f��� �ai� ����������aphic ����i��s i� ����v���ia��<br />
���pi����� Di�a�ic�� Pa����ia� a�� P� ����i��. H�w��v�����<br />
�ivisi�� �f �h�� Di�a�ic a�� ���pi��� ����i��s i���<br />
�w� s������i��s acc���i�� �� sp��ci��s ass������a���s<br />
si�i��a�i�y was ��� as ��vi��s as �ivisi�� i��� �ai�<br />
four regions, despite the first class indicator species<br />
i� ��ach �f s������i��s �Fi�s. 6-7�. N��v����h������ss��<br />
����������aphic �issi�i��a�i�y �f �h�� s������i��s was<br />
confirmed by different numbers of species found<br />
at each subregion:<br />
a� ���pi��� ����i��; I� �h�� W��s� a��pi��� s������i��s<br />
128 sp��ci��s w����� ���c������ wh�����as i� �h�� Eas�<br />
a��pi��� ����y 81 sp��ci��s.<br />
�� Di�a�ic ����i��; I� �h�� E��i�a�ic s������i��<br />
141 sp��ci��s w����� ��������i������ wh�����as i� �h��<br />
�������i�����a���a�-�i�a�ic s������i�� 107<br />
sp��ci��s.<br />
Acknowledgement<br />
Th�� a��h�� w����� ��i��� �� �ha�� a���� c�������a����s<br />
f��� �h�� ����v���ia� ��s���� �f Na���a�� His���y��<br />
Bi����ch�ica�� Fac����y U�iv���si�y �f �j����ja�a��<br />
E�vi��������a�� �����cy �f �h�� R��p����ic �f<br />
����v���ia a�� a���� ��h��� c�������a����s wh� c�������c����<br />
the caddisflies. The author also acknowledges<br />
�h�� Na���a�� His���y ��s���� �f ����������� f��<br />
���a���i�� hi� �h�� pa��icipa�i�� a� �h�� c��f������c��.<br />
References<br />
Ba�a���sc� P. 1990. - Z��������aphy �f f���shwa����s.<br />
V���. 1. G������a�� �is��i���i�� a�� �isp���sa�� �f<br />
Freshwater Animals. Wiesbaden, Aula Verlag:<br />
1–511.<br />
Ba�a���sc� P. 1972. - Typ��s �f �is��i���i��s a����<br />
freshwater animals. Rev. Roum. Boil. – Zool.,<br />
17, 3: 23–30.<br />
Carnelutti J. 1992. - Rdeči seznam ogroženih<br />
metuljev (Macrolepidoptera) v Sloveniji.<br />
Varstvo narave 17: 61-104.<br />
Hadži J. 1931. - Zoogeografska karta kraljevine<br />
Jugoslavije. Zbirka karata geografskog društva,<br />
B�����a�.<br />
Illies J. 1978. - Limnofauna Europaea. 2. Auflage.<br />
Stuttgart, New �ork, Gustav Fischer Verlag:<br />
�32 pp.<br />
Malicky H. 1987. - Anflugdistanz und� Fallenfang-<br />
Fa�������fa��barkeit<br />
von Köcherfliegen (<strong>Trichoptera</strong>) bei<br />
Lichtfallen. Jber. Biol. Stn. Lunz, 10: 140–157.<br />
Mršić N. 1997. - Živali naših tal. Uvod v pedozoologijo<br />
- sistematika in ekologija s splošnim<br />
pregledom talnih živali. Ljubljana, Tehniška<br />
založba Slovenije: 416 pp.<br />
Perko D., Orožen-Adamič M. (ur.) 1998. - Slovenija<br />
- P���aji��� i� ��j��j��. �j����ja�a�� ���a�i�s�a<br />
knjiga: 735 pp.<br />
Sket B. 2003. - Oblikuje se današnje živalstvo. V:<br />
Živalstvo Slovenije. Sket B., Gogala M., Kuštor<br />
V. (ur.). Ljubljana, Tehniška založba Slovenije:<br />
41–55.<br />
Urbanič G. 2003. - The impact of the light tube and<br />
�h�� �is�a�c�� �f �h�� ��i�h� ��ap f��� a s����a� ��<br />
a caddisfly (Insecta: <strong>Trichoptera</strong>) catch. Natura<br />
Sloveniae, 4, 1: 13–20.<br />
Urbanič G. 2004. - Ecology and distribution of<br />
caddisflies (Insecta: <strong>Trichoptera</strong>) in some<br />
wa����c���s��s i� ����v���ia. Diss����a�i�� �h��sis��<br />
U�iv���si�y �f �j����ja�a�� Bi����ch�ica�� Fac����y��<br />
189 pp.<br />
<strong>Ferrantia</strong> • 55 / 2008
R. Vieira-Lanero et al. The larva of Micrasema cenerentola Schmid, 1952<br />
The larva of Micrasema cenerentola Schmid, 1952<br />
(Insecta: <strong>Trichoptera</strong>: Brachycentridae)<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Rufino Vieira-Lanero, Marcos A. González, Fernando Cobo<br />
D��p�. Bi�����ía ��i�a��. U�iv���si�a��� U�iv���si�a��� ��� ��� �a��ia�� �a��ia�� ��� ��� C��p�s�����a<br />
C��p�s�����a<br />
1�782 �a��ia�� ��� C��p�s�����a.<br />
� C���ña ��pai��.<br />
�a��f�@�sc.��s<br />
�a��f�@�sc.��s<br />
Mª. José Servia<br />
Fac����a��� ��� Ci���cias. Ca�p�s �a Zapa���i�a s/�. U�iv���si�a��� �a C���ña.<br />
1�008 � C���ña ��pai��.<br />
Keywords: <strong>Trichoptera</strong>, Brachycentridae, Micrasema cenerentola, larval description, endemic,<br />
Iberian Peninsula.<br />
Abstract<br />
Th�� ��a�va �f Micrasema cenerentola Sch�i��� 19�2�� a�<br />
�������ic �f �h�� I����ia� P���i�s���a�� is ���sc�i���� f�� �h��<br />
first time. Among the European species of this genus,<br />
�h�� ��a�va �f M. cenerentola is �h�� ����y wi�h �w� ���s����a��<br />
sclerites and a strongly flattened head in combination.<br />
Résumé<br />
�a ��a�v�� ��� Micrasema cenerentola �ch�i��� 19�2�� ��<br />
������iq��� ��� ��a P��i�s����� I���iq����� ��s� ��c�i��� p���<br />
��a p����iè��� f�is. Pa��i ����s ��spèc��s �����p�������s ���<br />
c�� ��������� ��a ��a�v�� ��� M. cenerentola c´��s� ��a s������� q�i<br />
p�ss�� ����� sc����i���s ��s����a����s ��� ���� ��� f����������<br />
Zusammenfassung<br />
Di�� �a�v�� v�� �ic�as���a c�������������a �ch�i��� 19�2�� ��i�<br />
E�����i� ���� I����isch��� Ha���i�s������ wi�� ���� ���s���� �a��<br />
���sch�i������. I� V��������ich ���� �����päisch��� ������ �i��s���<br />
Gattung ist die Larve von M. cenerentola die Einzige, die<br />
�i�� K���i�a�i�� v�� ���s����a���� �������i���� ��� ��i����<br />
Introduction<br />
O��� �f �h�� ��s� �ic���ish p��������s �����a���� ��<br />
�h�� �a�����y �f E���p��a� T�ich�p����a is �ha�<br />
��s� �f �h�� I����ia� a�� Py������a� sp��ci��s �f �h��<br />
�����s Micrasema, significant inhabitants of rhitral<br />
ha�i�a�s�� a��� p�����y ���w� �� �his �ay a�� ���<br />
c����a���y �is�i���ish����� ���h ��a�va�� a�� a�����s.<br />
�cc���i�� �� G��������� ��� a��. �1992� a�� Vi��i�a-<br />
�a����� �2000��� �h�� �����s Micrasema is ���p���s�������<br />
i� �h�� I����ia� P���i�s���a �y M. cenerentola �ch�i���<br />
Typica�� ��a�va�� a�� p�pa�� cas��s a��� �a��� �f sa��; p�pa��<br />
cases show a characteristic lateral opening for water flow<br />
i�p��v�������. Th�� ha�i�a� �f �his sp��ci��s s�����s �� ���<br />
���s��ic���� �� s�a���� �����ai� �����s.<br />
ap��a�i�� ��� ass�cia�i��. ���s f������a�� ��a�vai���s ��� p�pa����s<br />
�ypiq���s s��� fai�s ��� sa�����; c����-ci ��������� ����<br />
��v�������� ��a���a���� ca�ac���is�iq��� p��� ���a����i��a�i�� ���<br />
l´écoulement de l�eau. L�habitat de cette esp�ce semble<br />
ê���� ��i�i�� à ���s p���i�s ��iss��a�� ��� ����a����.<br />
stark abgeflachten Kopf aufweist Die typischen Larval-<br />
��� P�pp����öch��� ���s���h��� a�s �a��; si�� ���si������ ��i���<br />
charakteristische laterale Öffnung, die der Verbesserung<br />
des Wasserabflusses dient. Das Habitat dieser Art<br />
sch��i�� a�f �����i��� B�����äch�� ���sch�ä��� ��� s��i�.<br />
19�2�� M. longulum �c�ach��a��� 1876�� M. minimum<br />
�c�ach��a��� 1876�� M. morosum ��c�ach��a��� 1868�<br />
a�� M. servatum �Navás�� 1918�. � sp��cia�� p��������<br />
is �ha� �f Micrasema moestum (Hagen, 1868): under<br />
�his �a��� �w� c�yp�ic sp��ci��s �i�h� ��� c��c��a�����.<br />
������v����� i� a ���c���� ���vi��w �f �h�� Micrasema<br />
sp��ci��s ��ivi�� i� �h�� I����ia� P���i�s���a a�� Py��������s��<br />
B���sa���a�� & G��������� �2006� c��c������� �ha� ���h<br />
Micrasema salardum �ch�i��� 19�2 a�� Micrasema<br />
vestitum Navás�� 1918�� a��� "���� sp��ci��s" a�� ��s�<br />
��� a����� �� �h�� p���vi��s ��is�.<br />
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134<br />
Th�� ��a�va�� �f s���� �f �h��s�� I����ia� sp��ci��s hav��<br />
been described by different authors (see Vieira-<br />
�a����� ��� a��.�� 1998� ��� a� �h�� ������� �h�� ��a�va��<br />
�f M. cenerentola�� M. salardum a�� M. vestitum��<br />
����ai� s�i���� �����sc�i����. I� �his pap��� �h�� ��a�va<br />
�f Micrasema cenerentola is described for the first<br />
�i���.<br />
Material and methods<br />
����� y��a�s a���� w�� c�������c���� 100 ��as� i�s�a�<br />
��a�va�� a�� 201 p�pa�� �f Micrasema sp. f��� �w�<br />
small mountain brooks –Cabanas Vellas and Río<br />
de la Vara– located in Sierra de Ancares (Lugo,<br />
Galicia, NW Spain). We have confirmed that our<br />
unidentified pupae (and, therefore, also the larvae)<br />
�������� �� �h�� sp��ci��s M. cenerentola. I� �his pap��� w��<br />
describe the final instar larva of this species. Setal<br />
������c��a����� a�� �����i������y f������ws Wa����ac�� et<br />
al. �1990� a�� Wi����ia�s & Wi��i�s �1981�.<br />
Description of the final instar<br />
larva<br />
B��y �������h �.3 - �.8 �� �N = 20�. G������a��<br />
app��a�a�c�� �ypica�� �f �h�� �����s �Fi�s. 1-3�.<br />
Head capsule: ���a� h��a� �������h 0.66 �� �N = 20�.<br />
H��a� �����ish-ch��s���� i� c�������� �������� i� ���sa��<br />
vi��w �Fi�.4� ��� s��i�h���y �������� �ha� wi���. D��s��<br />
flattened (Figs. 1-3, 6-9), even slightly concave at<br />
eye level, and with a fine, granular ornamentation<br />
c�v���i�� �h�� s��fac�� �Fi�. 4��� ���c��p�i�� ��<br />
the muscle attachment spots. A conspicuous<br />
���s���a����a���� s�p�a�c���a� �i���� a�is�� a����� ��ach<br />
si����� a�� a��s� a -sh������ a�� ����ss c��spic���s-<br />
��a����a�� i�f�a�c���a� �i���� is p���s���� �Fi�. 7 a a�� ���<br />
���sp��c�iv����y�. P�s����i�� pa�� �f �h�� h��a� caps�����<br />
angled when viewed in profile (Fig. 8).<br />
V�����a�� si��� �f �h�� h��a� caps����� s��i�h���y pa����� �ha�<br />
���s��. ������i�� v�����a�� ap������ q�a��a�����a���<br />
��������i�� f��� �h�� ��a�� �a��i� �� �h�� a���a��<br />
f��a���� �Fi�. ��. ��������a�� sc�����i���s q�a��a�����a���<br />
pai������ ��ach wi�h a si������ s���a. �������a�� sh�����<br />
i�c��spic���s i� ���sa�� vi��w.<br />
����a 18 s�a���� a�� i�s������� c���s�� �� �h�� p�s����i��<br />
�a��i�; s���a�� 17 a�� 3-6 hya��i���; s���a�� 2 a�� 3<br />
�if��ca���� a� ap���.<br />
Thorax: Pronotum trapezoidal in dorsal view<br />
�Fi�s. 8�� 9��� �h�� a�����i�� �a��i� wi����. � �is�i�c���<br />
c��v����� ��a�sv���s�� �i���� is p���s���� ����i�� f���<br />
���� a��������a����a�� �a��i� �� �h�� �pp�si��� ac��ss<br />
�h�� c�����a�� p�i�� �f �h�� ���s��. F��� s����� a��<br />
s��v���a�� s�a���� s���a�� a��� i�s������� �� �h�� ������ �f �h��<br />
�his ca�i�a. ������i�� �a��i� �f p������� s��i�h���y<br />
c��v��� ��w�wa��s a�� c�v������ wi�h s�a���� s���a����<br />
s���� �f �h��� p�i��i�� �pwa��s�� ��� ��s� �f<br />
�h��� �hi����� a�� ����� ��w�wa��s. H���isc�����i���s<br />
ch��s���� c����������� �a����� ah��a� �h�� �i����.<br />
���s������ ch��s���� ���w� �Fi�s. 8-10��� pa�����<br />
�ha� p������� a�� c�v������ wi�h �w� sc�����i���s��<br />
��ach wi�h a �a�� ����iq��� ��i��� ��a����a����y. E�c��p�i��<br />
�h�� a���a p��ac��� ���hi�� �his ��i����� ��ach h���isc�����i���<br />
is c�v������ wi�h �8 - 68 s���a��; s���� �f �h��� a���<br />
i�s������� �� �h�� a�����i�� �a��i� a�� hya��i����� ���<br />
��s� �f �h��� a��� �a�� c���������.<br />
����a���s�� �Fi�s. 8�� 9� ������a���s wi�h 2 pai�s<br />
�f s�a������ ch��s���� c����������� sc�����i���s; ����ia�<br />
sc�����i���s wi�h � - 6 s���a��; ��a����a�� sc�����i���s ��ia�����a�����<br />
wi�h a �a���� ����iq��� ��i��� ����ia����y a�� 18 - 20 s���a��<br />
p��ac��� �� �h�� a�����i�� �a��i�.<br />
Prothoracic legs (Fig. 12): shorter than meso- and<br />
����a�h��acic �����s. � p���yf��ca��� s���a is i�s�������<br />
�� ���h a�����i�� a�� p�s����i�� fac��s �f �h�� c��a.<br />
V�����a�� �a��i� �f p���i�a�� s�������� �f ���cha�����<br />
wi�h s��v���a�� �ic��spi���s �as i� Fi�. 11� a�� a<br />
�is�a�� s���a; �is�a�� s�������� wi�h a p���yf��ca��� s���a<br />
�� �h�� p�s����i�� fac���� �w� v�������is�a�� sp��s a��<br />
s��v���a�� s����a���� s���a�� a����� �h�� v�����a�� �a��i�.<br />
P���h��acic f����� wi��� a�� sc��� wh��� c��pa����<br />
wi�h �h�� �i�ia. Th�� s�a���� v�����a�� �a��i� ���a�s 4 - �<br />
s���� sp��s�� 4 - � s����� s���a�� ���i�h� c��������� a��<br />
v���y si�i��a� �� sp��s� a�� s��v���a�� s����a���� s���a��.<br />
P�s����i�� fac�� wi�h a p���yf��ca��� s���a. D��sa��<br />
�a��i� c�v������ �f �ic��spi���s a�� ���a�s 10 �����<br />
s���a�� �1 p���i�a�� a�� 9 �is�a�� s���a���.<br />
B��h v�����a�� a�� ���sa�� �a��i�s �f �h�� �i�ia�� a���<br />
f�����y c�v������ �y �ic��spi���s. Th�� ���sa�� �a��i�<br />
���a�s 4 �is�a�� s���a�� a�� �h�� v�������is�a�� �a��i�<br />
����y ���� sp�� a�� ���� s���a. Ta�si wi�h a ���s��is�a��<br />
s���a a���� v�������is�a����y�� � s����� sp��s a�� a �is�a��<br />
s���a. Ta�sa�� c��aw a�� �i�ia si�i��a� i� �������h�� �asa��<br />
s���a ����h��y ���c�����i�� ha��f c��aw �������h.<br />
Mesothoracic legs (Fig. 13): ventral margin of<br />
c��a���� ���cha����� a�� �a�si c�v������ �f �ic��s���a��.<br />
� ����p �f �h����� p���yf��ca��� s���a�� a��� i�s������� ��<br />
�h�� a�����i�� si��� �f �h�� c��a. V�������is�a�� �a��i�<br />
�f ���cha����� wi�h a ����p �f s����a���� s���a��. B��h<br />
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R. Vieira-Lanero et al. The larva of Micrasema cenerentola Schmid, 1952<br />
Figs. 1 – 5: M. cenerentola, final instar larva. 1 Larval case and larva in lateral view. 2 Habitus, lateral view .<br />
3 Habitus, dorsal view. 4 Head capsule, dorsal view . 5 Head, a detailed view of the anterior ventral apotome.<br />
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R. Vieira-Lanero et al. The larva of Micrasema cenerentola Schmid, 1952<br />
Figs. 6 – 11: M. cenerentola, final instar larva. 6 Head, lateral view. 7 Right lateral sclerite of head showing the<br />
dorsolateral, supraocular ridge (a) and the lateral infraocular ridge (b). 8 Anterior half of larva in lateral view.<br />
9 Anterior half of larva in dorsal view. 10 Right mesothoracic hemisclerite. 11 Microsetae and microspines on the<br />
metathoracic femur.<br />
136<br />
<strong>Ferrantia</strong> • 55 / 2008
R. Vieira-Lanero et al. The larva of Micrasema cenerentola Schmid, 1952<br />
Figs. 12 – 17: M. cenerentola, final instar larva. 12 Prothoracic leg, lateral view. 13 Mesothoracic leg, lateral<br />
12 Prothoracic leg, lateral view. 13 Mesothoracic leg, lateral<br />
view. 14 Metathoracic leg, lateral view. 15 Abdominal segments VIII and IX in dorsal view. 16 Idem in ventral view.<br />
17 Idem in lateral view.<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
137
R. Vieira-Lanero et al. The larva of Micrasema cenerentola Schmid, 1952<br />
138<br />
Figs. 18 – 23: M. cenerentola, final instar larva. 18 Right anal claw in lateral view. 19 Detail of the anal claw in<br />
ventral view showing the stout main claw and two dorsal accessory hooks. 20 Detail of the anal claw in lateral<br />
view. 21 Mass of pupal cases; note the lateral openings (arrow). 22 The opposite side of the same mass of pupal<br />
cases. 23 Pupal cases, and line drawings of the multiperforated membrane (a) and the posterior opening (b).<br />
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R. Vieira-Lanero et al. The larva of Micrasema cenerentola Schmid, 1952<br />
v�����a�� a�� ���sa�� �a��i�s �f �h�� f�����a a�� �i�ia��<br />
c�v������ �y �ic��spi���s. ������i�� fac�� �f f�����<br />
wi�h ���� p���yf��ca��� s���a�� ���sa�� �a��i� wi�h a<br />
����p �f 7 s���a�� �2 p���i�a�� a�� � �is�a�� s���a���;<br />
v�������is�a����y �h����� is a s������� hya��i��� s���a. Ti�ia<br />
wi�h 4 s���a�� �� �h�� ���sa�� �a��i� a�� ���� s�������<br />
hya��i��� s���a �� �h�� v�������is�a�� �a��i�. ������i��<br />
si��� �f �h�� �a�si c�v������ �f �ic��spi���s; ���sa��<br />
�a��i� wi�h 2 s���a���� v�����a����y wi�h 3 sp��s �����<br />
����ia� a�� 2 �is�a���. Basa�� s���a s�a����.<br />
Metathoracic legs (Fig. 14): ventral margin covered<br />
�f �ic��spi���s i� a���� �h�� ����� s��������s�� a�� a��s�<br />
�� �h�� ���sa�� �a��i� �f f������� �i�ia a�� �a�s�s��<br />
a�� �� �h�� a�����i�� fac�� �f �i�ia a�� �a�s�s. Tw�<br />
p���yf��ca��� s���a�� a��� i�s������� �� �h�� a�����i�� fac��<br />
�f �h�� c�a�. T��cha����� wi�h a v�������is�a�� ���sh<br />
�f 10-12 s����a���� s���a��. ������i�� si��� �f �h�� f�����<br />
wi�h ���� p���yf��ca��� s���a; p�s����i�� fac�� wi�h a<br />
�a���� �is�a�� s���a. V�����a�� �a��i� wi�h 2 s�������<br />
hya��i��� s���a��; ���sa�� �a��i� wi�h a ����p �f 8-<br />
9 s���a�� �1 p���i�a�� a�� 7-8 �is�a�� s���a���. D��sa��<br />
�a��i� �f �i�ia�� wi�h 4 s���a�� �2 ����ia� a�� 2<br />
�is�a�� s��a������ a�� v�����a�� �a��i� wi�h ���� �is�a��<br />
sp��. Th�� ���sa�� �a��i� �f �h�� �a�s�s ���a�s 2 �is�a��<br />
s���a��; �h�� v�����a�� �a��i� ���� ����ia� sp�� a�� a<br />
�is�a�� ����p �f 3 s�a���� sp��s. Ta�sa�� c��aw si�i��a�<br />
�� ���s��h��acic c��aw.<br />
�������� ���a���y cy��i���ica�� a�� p�s����i�� ha��f<br />
��a��a����y �ap�������� �i��h s�������� c����a���y �hi�����<br />
�Fi�s. 2�� 3�. �����i�a�� �i����s a�s����. D��sa�� h��p<br />
a�s���� a�� ��a����a�� h��ps i��is�i�c� i� s�������� I.<br />
���������s II-VIII wi�h a ��a����a�� ��i��� c��p�s��� �f a<br />
����p �f 14 - 23 ��a����a�� ������c����s a�� a s�a���� s���a<br />
�� ��ach si���.<br />
Mid dorsal sclerite of segment IX (Fig. 15) weakly<br />
sclerotized, elliptical, with 16 setae different in size<br />
a����� p�s����i�� �a��i�. O��� ��a����a�� s���a is p��ac���<br />
on the soft cuticle, outside this sclerite.<br />
D��sa�� si��� �f a�a�� p�������s �Fi�s. 1�-17� a����s�<br />
c��p���������y ������a���s; p�s����i�� ���sa�� �a��i�<br />
with 17 setae: 12 small and thin and 5 long, stout,<br />
�a�� s���a��. V�����a�� si��� ������a���s�� c�v������<br />
wi�h �ic��-spi���s. � pai� �f �a�-��i��� sc�����i���s ca�<br />
��� �is�i���ish��� �� ��ach si��� �f �h�� a�a�� �p���i��.<br />
�a����a�� sc�����i��� w��a���y sc�������i�����. ��a�� c��aw<br />
�Fi�s. 18-20� wi�h �w� s�a���� acc��ss��y h���s�� �h��<br />
i����� s�a������� �ha� �h�� ������.<br />
Larval and pupal cases (Figs. 1, 21-23): The larvae<br />
��i��� a cy��i���ica���� s��ai�h��� s��i�h���y c��ica�� cas����<br />
wi�h a cha�ac����is�ic �a���w p�s����i�� �hi��. Typica��<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
cas��s a��� �a��� �f si��� a�� a va�ia����� p���c����a���<br />
�f sa��; as a ���s������ s���� cas��s p���s���� ��a���� si���y<br />
a���as a�� s���� ��h��� a��� ��s���y �a��� �f sa��. Th��<br />
posterior third is usually made of fine sand grains<br />
a�� �h�� p�s����i�� �p���i�� is ����y pa��ia����y c���s���<br />
�y f��� �hi��� si��� �������si��s �Fi�. 23��.<br />
Pupal cases are modified larval cases, improved<br />
for a better water flow through the pupal case<br />
�s���� ��c�����ica�� �����s�. Dis�i�c�iv����y�� �h�� ��as�<br />
i�s�a� ��a�va�� ��i��� a� i������a���� �����ip���f��a����<br />
������a��� �Fi�. 23a� j�s� a��v�� �h�� cas�� �a���wi����<br />
a�� �p��� a s�a���� h����� i� �h�� wa���� ���hi�� i� �s���� �h��<br />
a���w i� Fi�. 21��� �����pi�� �h�� p�s����i�� �p���i��<br />
unmodified.<br />
Discussion<br />
�cc���i�� �� �h�� ������� �f ���s����a�� sc�����i���s<br />
�f �h�� ��as� i�s�a� ��a�va�� �w� ����ps ca� ���<br />
�is�i���ish��� a���� �h�� I����ia� sp��ci��s �f �h��<br />
genus: a group of larvae with two mesonotal<br />
sc�����i���s �c��p�isi�� M. cenerentola�� M. morosum<br />
a�� M. longulum� a�� a ����p wi�h f��� ��h��<br />
����ai����� ���w� sp��ci��s�.<br />
Th�� ��a�va �f M. cenerentola ca� ��� ��asi��y<br />
�is�i���ish��� f��� �ha� �f M. morosum a�� M.<br />
longulum by its strongly flattened head (see Table I<br />
f�� a��i�i��a�� cha�ac����s�.<br />
An interesting finding from this research is that<br />
�h�� ��a�va�� �f s���� sp��ci��s �f �his �����s a��� �����<br />
��asi��y �is�i���isha����� a���� �h���s����v��s �ha�<br />
a�����s a���. F�� i�s�a�c���� �h�� a�����s �f M. servatum<br />
a�� M. cenerentola a��� v���y ��ch a��i����� whi���� �h��<br />
larvae are clearly different and, seemingly, belong<br />
to different groups.<br />
Notes on distribution and<br />
ecological preferences<br />
Th�� ��a�va�� �f M. cenerentola w����� c�������c���� ����y<br />
i� s�a���� �����ai� �����s ���ca���� a� 11�0-1380 �.<br />
a.s.��. Th��y w����� f���� i� ��a���� �������s �� �h��<br />
������si��� �f �i� s�����s p��ac��� j�s� ���f���� s�a����<br />
waterfalls. The larvae usually attach the anterior<br />
������� �f �h�� cas�� �� �h�� s��s��a��� wi�h a s��c����i��<br />
�isc�� av�i�i�� �� ��� wash��� ��w�s����a�.<br />
139
R. Vieira-Lanero et al. The larva of Micrasema cenerentola Schmid, 1952<br />
140<br />
Table I: Some other characters that can be useful when separating the larvae of the known Iberian<br />
species of the genus Micrasema with two mesonotal sclerites (see Waringer & Graf, 1997; pg.<br />
133, fig. 2; and pg. 135, fig.7).<br />
M. cenerentola M. morosum M. longulum<br />
���������a����a�� �a��i� �f ���s����a��<br />
sc�����i���s<br />
���������� s��i�h���y<br />
a�������<br />
�������� ����������� a�����i����y<br />
Head, occipital area in profile a������� �������� ��������<br />
V�������is�a�� ������ �f ���s�- a�� ���- wi�h��� c��ica�� wi�h��� c��ica�� wi�h a c��ica��<br />
�a�h��acic �a�si<br />
p��j��c�i��<br />
p��j��c�i��<br />
p��j��c�i��<br />
Cas��<br />
sa�� ��ai�s a��<br />
si���<br />
v������a�� f�a������s<br />
a��a����� i� spi�a��<br />
����y si���<br />
They often aggregate for pupation, selecting areas<br />
with heavy current and attaching the anterior<br />
�p���i�� �f �h�� cas�� �� �h�� s��s��a��� wi�h ���� ��<br />
����� s�a������ �iscs. �a���� �������s �f p�pa�� cas��s<br />
hav�� ������ f���� ������h����� a��a����� i� ���� �� �w�<br />
����v����s a�� ���s����i�� i� a c��pac� s���c����� �Fi�s. 21��<br />
22�. This p��c���ia� a��a��������� ca� ��� fav������ if<br />
water flow to he case is made through the small hole<br />
�p������ �y �h�� ��as� i�s�a� ��a�va i� �h�� cas�� wa����.<br />
M. cenerentola is a� �������ic �f �h�� I����ia� P���i�s���a<br />
�B���sa���a�� a�� G����������� 2006�. Th�� sp��ci��s<br />
was p���vi��s��y ci���� ����y �y �ch�i� �19�2� f���<br />
the type locality (Avila, Central Spain). Afterwards<br />
we have been the only to find it in a few sampling<br />
si���s�� a���� ���ca���� i� �i����a ��� ��ca���s a�� �i����a ��<br />
Ca������ ������� NW �pai��.<br />
Acknowledgements<br />
This s���y was s�pp������ �y �h�� p��j��c�<br />
PGIDTI07PXIB200030PR. Facilities needed for<br />
�his w��� w����� p��vi���� �y �h�� "E�c��� �� C��"<br />
Hy����i�����ica�� Fi����� ��a�i��.<br />
References<br />
B���sa���a�� �. & G��������� �. �. 2006. - U�<br />
di���cile probl�me de taxonomie: les Micrasema<br />
(<strong>Trichoptera</strong>: Brachycentridae) des eaux<br />
c���a����s ��� ��a P��i�s����� I���iq��� ��� ���s<br />
Py������s. ���a����s ��� ��a ��ci��� E���������iq���<br />
de France. (n. s.), 42 (1): 119-127<br />
G����á������ �. �.�� T����a �. �. W.�� Ga�cía ��� Ja��ó� D.��<br />
& Cobo F.1992. - Lista faunística y bibliográfica<br />
��� ���s T�icóp�����s �T�ich�p����a� ��� ��a P���í�s���a<br />
I���ica �� Is��as Ba����a���s. �s�ciació� ��spañ���a<br />
de Limnología. Listas de la flora y fauna de<br />
��as a��as c���i�����a����s ��� ��a P���í�s���a I���ica��<br />
Publ. nº 11: 200 p.<br />
Vi��i�a-�a����� R. 2000. - �as ��a�vas ��� ���s T�icópteros<br />
(Insecta: <strong>Trichoptera</strong>) de Galicia. PhD<br />
U�iv���si�a��� ��� �a��ia�� ��� C��p�s�����a. 611<br />
pp.<br />
Vi��i�a-�a����� R.�� G��������� �. �. & C��� F. 1998.<br />
- Th�� ��a�va �f �ic�as���a s���va��� �Navás��<br />
1918� �T�ich�p����a; B�achyc�����i�a���. G�a������sia��<br />
54: 3-8.<br />
Wa����ac�� I. D.�� Wa����ac�� B. & Phi��ips�� G. N. 1990. - �<br />
���y �� �h�� cas��-���a�i�� ca��is ��a�va�� �f B�i�ai�<br />
a�� I�����a��. F���shwa���� Bi�����ica�� �ss�cia�i��.<br />
Scientific Publication 51: 1-237.<br />
<strong>Ferrantia</strong> • 55 / 2008
J. Waringer, W. Graf Light-trapping of <strong>Trichoptera</strong> at the March<br />
Light-trapping of <strong>Trichoptera</strong> at the March, an<br />
eighth-orderAustrian lowland river<br />
Poster Abstract<br />
������ T�ich�p����a w����� ca��h� f��� 26 ���p����������<br />
2001 �� 7 N�v��������� 2002 a� �h�� �a��s �f �h��<br />
March River at Angern, Lower Austria (16° 50�<br />
05��E; 48° 22� 44�� N; 144 m above sea level), using<br />
a J����y-�yp�� ��i�h� ��ap. F��� a ���a�� �f 36��780<br />
sp��ci����s ca��h��� �h�� ��s� a����a�� sp��ci��s w�����<br />
Hydropsyche bulgaromanorum �a��ic�y�� Hydropsyche<br />
contubernalis �c�ach��a��� Setodes punctatus<br />
�Fa��ici�s��� Ceraclea dissimilis �����ph���s��� Ceraclea<br />
albimacula �Ra����� a�� Hydropsyche modesta<br />
Navas �Ta�. 1�. N��a���y a���� sp��ci��s c�������c���� a� �h��<br />
�a�ch sh�w ��a���� �is��i���i��a�� �a����s�� �a�y �f<br />
�h��� c�v���i�� wh����� E���p��.<br />
In five out of the thirteen most abundant species<br />
the sex ratios significantly differed from 1:1, with<br />
a� ���c��ss �f �a����s i� H. modesta a�� S. punctatus<br />
a�� a� ���c��ss �f f���a����s i� Agapetus laniger��<br />
Orthotrichia costalis a�� Ecnomus tenellus.<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Johann Waringer<br />
D��pa������� �f F���shwa���� Ec�����y�� Vi����a Ec�����y C�������<br />
U�iv���si�y �f Vi����a<br />
����ha�s��a�� 14<br />
�-1090 Vi����a<br />
j�ha��.wa�i�����@��ivi��.ac.a�<br />
Wolfram Graf<br />
D��pa������� �f Wa������ ����sph����� & E�vi��������<br />
U�iv���si�y �f Na���a�� R��s���c��s & �pp��i��� �if�� �ci���c��s<br />
�a�-E�a������-���a�� 17<br />
�-1180 Vi����a<br />
w���f�a�.��af@����.ac.a�<br />
Of �h�� �������������ica�� pa�a�������s ���s������ ����y<br />
s��s��� a�� �i��i�h� ai� ����p���a�����s as w������ as<br />
precipitation had significant (P< 0.05) effects on<br />
total catch. The longitudinal classification of the<br />
sampling station based on species-specific zonal<br />
distribution patterns of caddisflies yielded highest<br />
sc����s i� �h�� ��pi- a�� ����ap��a�a�� ����i��.<br />
Wi�h ���sp��c� �� f��c�i��a�� f�����i�� ����ps��<br />
passive filtering collectors made up to 48.5 % of<br />
the total catch, reflecting the high proportion<br />
�f Hy���psych�� sp��ci��s. Th�� s��c��� a�� �hi��<br />
��s� a����a�� f�����i�� ����ps w����� p����a���s<br />
�29.�%� a�� ��a�����s �19.7%�. C���i���� wi�h �h��<br />
���w p���c����a��� �f sh��������s �1.1% �f �h�� ���a�����<br />
the species inventory reflects the shift from coarse<br />
to fine particulate organic matter downstream, as<br />
s�����s���� �y �h�� Riv��� C���i���� C��c��p�.<br />
141
J. Waringer, W. Graf Light-trapping of <strong>Trichoptera</strong> at the March<br />
Table 1: <strong>Trichoptera</strong> species caught by a light trap on the banks of the March River at Angern, Lower Austria, from<br />
26 September, 2001 to 7 November, 2002; showing the species, probable breeding habitat (M= March River, S=<br />
standing waters of the floodplain), total number of individuals caught (n; males and females), percentage of total<br />
catch (%) and times when species were present in the trap. Species are arranged in taxonomic order. Another four<br />
species (Agraylea multipunctata Curtis, 1834, Hydroptila simulans Mosely, 1920, Hydropsyche bulbifera McLachlan,<br />
1878, Trichostegia minor (Curtis, 1834)) were collected by W. Graf at a March station ten kilometres to the<br />
south in August, 2004. Bold characters: Larvae collected in the March.<br />
142<br />
Species Habitat Males/females % Flight period<br />
Glossosoma boltoni C���is�� 1834 � 1 / 0 2� J���<br />
Agapetus laniger �Pic������1834� � 16 / 37 0.14 20 Jun – 25 Jul<br />
Agraylea sexmaculata C���is�� 1834 � 1 / 2 0.01 20 Jun – 28 Aug<br />
Hydroptila sparsa Curtis, 1834 � 23 / 28 0.17 15 May – 11 Sep<br />
Oxyethira flavicornis �Pic������ 1834� � 0 / 3 0.01 20 J��<br />
Orthotrichia costalis �C���is�� 1834� � 0 / 21 0.06 20 Jun – 27 Jun<br />
Orthotrichia tragetti ��s����y�� 1930 � 0 / 1 21 ���<br />
Psychomyia pusilla (Fabricius, 1781) � 26 / 26 0.14 22 May – 11 Sep<br />
Ecnomus tenellus �Ra������ 1842� ��� � 6 / 31 0.10 29 May – 30 Oct<br />
Cyrnus crenaticornis �K������a�i, 1859) � 1 / 0 29 May – 30 Oct<br />
Holocentropus stagnalis �����a��a�� 1874� � 0 / 1 22 �ay<br />
Neureclipsis bimaculata (Linnaeus, 1758) � 28 / 2� 0.14 1 �ay<br />
Hydropsyche bulgaromanorum Malicky, 1977 � 42�6 / 3003 19.74 8 May – 24 Oct<br />
Hydropsyche contubernalis McLachlan, 1865 � 11922 / 1�733 7�.19 1 May – 7 Nov<br />
Hydropsyche incognita Pi�sch�� 1993 � 1 / 0 2� J���<br />
Hydropsyche modesta Navas, 1925 � 134 / 33 0.4� 8 May – 2 Oct<br />
Hydropsyche pellucidula �C���is�� 1834� � 1 / 0 22 �ay<br />
Phryganea grandis �i��a���s�� 17�8 � 1 / 0 18 J���<br />
Brachycentrus subnubilus Curtis, 1834 � 2 / 2 0.01 1 May – 8 May<br />
Glyphotaelius pellucidus �R�����i�s�� 1783� � 1 / 0 17 Oc�<br />
Grammotaulius nigropunctatus �R�����i�s�� 1783� � 2 / 2 0.01 26 Sep – 17 Oct<br />
Limnephilus affinis C���is�� 1834 � 2 / 13 0.04 26 Sep – 24 Oct<br />
Limnephilus auricula C���is�� 1834 � 1 / 2 0.01 8 May – 30 Oct<br />
Limnephilus decipiens �K������a�i�� 1848� � 1 / 0 23 Oc�<br />
Limnephilus flavicornis �Fa��ici�s�� 1787� � 2 / 1 0.01 27 Jun – 24 Oct<br />
Limnephilus lunatus C���is�� 1834 � 1 / 1 0.01 10 Oct – 7 Nov<br />
Limnephilus vittatus �Fa��ici�s�� 1798� � 1 / 0 16 Oc�<br />
Halesus tesselatus �Ra������ 1842� � 1 / 0 17 Oc�<br />
Stenophylax permistus �c�ach��a��� 189� � 8 / 4 0.03 8 May – 24 Oct<br />
Goera pilosa �Fa��ici�s�� 177�� � 0 / 4 0.01 15 May – 20 Jun<br />
Athripsodes cinereus (Curtis, 1834) � 6 / 7 0.04 20 Jun – 11 Sep<br />
Ceraclea albimacula �Ra������ 1842� � 88 / 10� 0.�2 6 Jun – 21 Aug<br />
Ceraclea annulicornis �����ph���s, 1836) � 1 / � 0.02 22 May – 27 Jun<br />
Ceraclea dissimilis (Stephens, 1836) � 160 / 218 1.03 22 May – 3 Oct<br />
Leptocerus tineiformis C���is�� 1834 � 0 / 9 0.02 20 Jun – 25 Jul<br />
Oecetis furva �Ra������ 1842� � 2 / 1 0.01 20 Jun – 25 Jul<br />
Oecetis lacustris �C���is�� 1834� � 0 / 1 20 J��<br />
Oecetis notata (Rambur, 1842) � 9 / 10 0.0� 20 Jun – 14 Aug<br />
Oecetis ochracea (Curtis, 1825) � 3 / 2 0.01 22 May – 27 Jun<br />
Oecetis tripunctata (Fabricius, 1793) � 2 / 0 0.01 27 Jun – 25 Jul<br />
Setodes punctatus (Fabricius, 1793) � �39 / 172 1.93 6 Jun – 11 Sep<br />
Mystacides azurea ��i��a���s�� 1761� � 0 / 1 20 J��<br />
Mystacides longicornis ��i��a���s�� 17�8� � 0 / 16 0.0� 15 May – 11 Sep<br />
N������ �f sp��ci����s 17260 / 19�20<br />
N������ �f sp��ci��s 43<br />
<strong>Ferrantia</strong> • 55 / 2008
P. Wiberg-Larsen Overall distributional patterns of European <strong>Trichoptera</strong><br />
Overall distributional patterns of European<br />
<strong>Trichoptera</strong><br />
Abstract<br />
Th�� E���p��a� T�ich�p����a fa��a was a�a��ys��� f��<br />
overall patterns related to area, latitude and occurrence<br />
�f �����ai���s a���as�� ���sp��c�iv����y�� �si�� ch��c���is�s f���<br />
26 countries. There was a significant correlation between<br />
latitude and species richness: An increasing richness<br />
��i�� s���h f�� ����ic sp��ci��s�� ��� a� i�c���asi�� �ich���ss<br />
��i�� ����h f�� ������ic sp��ci��s. F���h����� �h�� �������<br />
of lotic species was significantly correlated with the<br />
Introduction<br />
N��a���y �hi��y y��a�s a���� B���sa���a�� & �a��ic�y<br />
�1978� c��pi����� �h�� ��s� ���c���� c��p���h���siv��<br />
ch��c���is� �f E���p��a� T�ich�p����a i�c����i��<br />
89� sp��ci��s �is��i������ a���� 27 ������aphic<br />
����i��s �s���� I����i��s 1978�. ��s� �f �h��s�� ������aphic<br />
����i��s�� �� ���c�����i��s��� hav�� ���c������y ������ �s���<br />
as �h�� ����p��a��� f�� �h�� Wa���� F�a���w��� Di���c�iv��<br />
�E���p��a� U�i�� 2000�. U�f�����a�����y�� �h��<br />
�is��i���i�� �f E���p��a� T�ich�p����a has ��� ������<br />
�p�a���� �� a� ��c�����i��a�� sca����. This ����s ���<br />
���a� �ha� fa��is�ics �f E���p��a� T�ich�p����a has<br />
������ ��������c���� i� ���c���� y��a�s. O� �h�� c����a�y�� a<br />
�����a�iv����y ����a� ������� �f ���w sp��ci��s hav�� ������<br />
������c���� a�� ���sc�i���� f��� �h�� a���a�� a�� �a�i��a��<br />
ch��c���is�s hav�� ������ p��vi���� �� ���vis��� f�� ��s�<br />
c�����i��s. I� a��i�i���� s���� �a�����ic ���visi��s<br />
hav�� �a���� p��ac���� a���h���h s���� sp��ci��s ����ps<br />
�ay s�i���� ������ a ca���f��� ���a�i�a�i��.<br />
Z��������aphica����y�� E���p�� s���s� I����i��s �1978�<br />
�ay h���� a����s� 1100 sp��ci��s. This is q�i��� a ��a����<br />
������� c��pa���� wi�h �h�� 16�3 sp��ci��s ���c������<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
Peter Wiberg-Larsen<br />
Na�i��a�� E�vi��������a�� R��s��a�ch I�s�i�����<br />
D��pa������� �f F���shwa���� Ec�����y<br />
U�iv���si�y �f �a�h�s<br />
V��j��søv��j 2��� P.O. B�� 314<br />
DK-8600 �i���������<br />
pw��@���.��<br />
occurrencesdel of mountainous areas. Overall patterns<br />
c����� a��s� ��� ������s��a���� �si�� �����i�i����si��a��<br />
sca��i�� �f si�i��a�i�y i��ic��s ����w����� �h�� ch��c���is�s��<br />
sh�wi�� �ha� �h�� fa��as �f �h�� s���h���� c�����i��s ���.�.<br />
G�����c���� P�����a�� + �pai��� a�� I�a��y� a��� ��ch �����<br />
different from each other than are the faunas of northern<br />
Europe. The relationships and patterns are discussed.<br />
f��� N���h �����ica i�c����i�� G��������a�� a��<br />
����ic� ����s�� 1993� �ha� ���p���s����s a ��ch ��a�����<br />
a���a a�� a s����wha� wi���� c��i�a�ic �a����. �<br />
c��pa�is�� ����w����� E���p�� a�� N���h �����ica<br />
a��� �������va���� as �h��y sha��� a����s� �h�� sa��� fa�i��i��s<br />
�f T�ich�p����a a�� ��a������y �h�� sa��� �����a�iv�� sp��ci��s<br />
�ich���ss �f �h��s�� fa�i��i��s �a���h���h ����y 33 sp��ci��s<br />
�cc�� i� ���h "����i��s"�. This si�i��a�i�y �ay��<br />
h�w��v����� ��� ��� s��p�isi�� as E���p�� a�� N���h<br />
�����ica w����� c�����c���� ���i�� a���� 120 �i����i��<br />
y��a�s a�� �i.��. ���i�� �h�� C����ac����s p���i���.<br />
Th�� �����a�iv����y hi�h sp��ci��s �ich���ss �f E���p��<br />
�a���s ����������aphica�� a�a��ys��s i�������s�i��.<br />
Th����� hav�� ������ s��v���a�� s���i��s �f �ha� �i����<br />
���a��i�� wi�h ����� �� ����ss ���s��ic���� ������aphica��<br />
areas (e.g. Malicky 1985; Pitsch 1993; Cianficconi,<br />
Moretti & Tucciarelli 1997; Laasonen, Laasonen<br />
& Ny��� 1998; Uh�����vich & N���a�i 1999;<br />
R������ 2001�. N� s���i��s�� h�w��v����� s����� �� hav��<br />
focussed on the overall patterns of the distribution<br />
�f E���p��a� T�ich�p����a �si�� s�a�is�ica�� ����h��s<br />
a�� ��h��� a�a��y�ica�� �����s. This is �h�� p��p�s�� �f<br />
�h�� p���s���� s���y �ha� p�i�a�i��y f�c�s��s �� �h��<br />
�is��i���i�� �� �h�� E���p��a� c���i�����.<br />
143
P. Wiberg-Larsen Overall distributional patterns of European <strong>Trichoptera</strong><br />
144<br />
Material and methods<br />
I� �h�� a�s���c�� �f s�i�a����� fa��is�ic �a�a f��� �h��<br />
E���p��a� ��c�����i��s a �a�as��� �si�� �h�� ��s�<br />
���c���� ch��c���is� f��� 26 c�����i��s was c��pi�������<br />
s�pp������������ �y a��i�i��a�� p����ish��� �� ��v���<br />
��p����ish��� ���c���s �Ta�. 1�. ����� �h��s��<br />
c�����i��s �pai� a�� P�����a�� w����� ���p���s�������<br />
�y a c����� ch��c���is� f�� �h�� I����ia� P���i�s���a.<br />
Su���ciently comprehensive data were not<br />
avai��a����� f�� �i�h�a�ia�� B����a��s�� U��ai����� a�� �h��<br />
f������ Y���s��avia ����c��p� ����v���ia�. Th�� c�����y<br />
�a�as���s w����� a�j�s���� ����y �� i�c������ sp��ci��s<br />
�cc���i�� �� �h�� c���i����� ����c��p� i� cas�� �f �h��<br />
U�i���� Ki����� a�� I�����a���. Th�s�� f�� ���a�p����<br />
sp��ci��s �cc���i�� �� �h�� I����ia��� F����ch a��<br />
I�a��ia� ch��c���is�s�� ��� ����y f���� �� �h�� is��a��s �f<br />
�a������ca�� C��sica a�� �a��i�ia/E���a�� ���sp��c�iv����y��<br />
were omitted. Accordingly, Greek species<br />
�cc���i�� ����y �� �h�� is��a�� �f �h�� ������a� ����i��<br />
or on Crete were omitted from the Greek dataset.<br />
B��i�� ���ca���� c���s�� �� �h�� I�a��ia� �ai���a�� �h��<br />
�ici��ia� Is��a�� was�� h�w��v����� ����a����� a pa�� �f<br />
�h�� c���i�����.<br />
I ����y i�c������� sp��ci��s�� a���h���h a ���� �f s��sp��ci��s<br />
c����� hav�� ������ �a���� i��� c��si����a�i��.<br />
�p��ci��s w����� �ivi���� i��� ����ic sp��ci��s �i.��. sp��ci��s<br />
p�i�a�i��y �cc���i�� i� ����i�� wa����s� a�� ������ic<br />
sp��ci��s �sp��ci��s p�i�a�i��y �cc���i�� i� ��a���s a�� p���s�.<br />
�p��ci��s f���� i� hy���phi����s ha�i�a�s ���.�. sp�i��s�<br />
was ���si��a���� as ����ic. Th�� fa�i��i��s ��c��psychi�a����<br />
B���a��i�a���� B�achyc�����i�a���� Ca��a��c���a�i�a����<br />
Dips�����psi�a���� G���ss�s��a�i�a���� Hy���psychi�a����<br />
G����i�a���� ���pi��s���a�i�a���� O�����c���i�a����<br />
Phi���p��a�i�a���� Rhyac�phi��i�a���� ����ic�s���a�i�a����<br />
U����i�a���� a�� ��s� sp��ci��s �f Psych��yii�a�� w�����<br />
����a����� as ����ic�� wh�����as Ec���i�a���� Ph�y�a���i�a��<br />
a�� ����a��i�a�� w����� ����a����� as ������ic. ���v���a�� �������a<br />
�f Hy���p�i��i�a���� �i����phi��i�a�� a�� P���yc������p��i�a��<br />
w����� c��si������� ����ic�� wh�����as s��v���a�� ��h��� sp��ci��s<br />
��������i�� �� �h��s�� fa�i��i��s w����� c��si������� ������ic.<br />
A significant number of species was designated as<br />
endemic. There is no precise definition of endemic<br />
sp��ci��s ����a��i�� �h�� si���� �f �h�� ���s��ic���� a���a i�<br />
which �h�� sp��ci��s a��� f����. Th�s �������a����y�� I hav��<br />
����a����� sp��ci��s f���� i� ����y ���� c�����y �� ��<br />
�h�� I����ia� P���i�s���a as �������ic. E�c��p�i��s a���<br />
�f c���s�� cas��s�� wh����� a sp��ci��s a��s� �cc��s ���si���<br />
�h�� 26 c�����i��s i� c��si����a�i��. This is �f c���s��<br />
a �a�h��� �i�i� app��ach as s���� sp��ci��s �ay ���<br />
�������ic �� ���s��ic���� �����ai� a���as c��ssi��<br />
c�����y �������s.<br />
G�����aphica�� �a�a i�c����i�� �h�� ���a�� a���a�� ���a�<br />
��a�i������� a�� a���a �f "hi�h" �����ai�s �f �h��<br />
respective countries were obtained from o���cial<br />
�aps a�� �a�a�as��s. Th�� ���a�� a���a �f F�a�c����<br />
I�a��y a�� G�����c�� was �����c��� �y �h�� a���a �f<br />
C��sica�� �a��i�ia�� C������ a�� �h�� ������a� Is��a��s��<br />
���sp��c�iv����y �acc���i�� �� �h�� c�����c�i�� �f �h��<br />
sp��ci��s ��is�s�� s���� a��v���. ���a� ��a�i����� f�� a �iv���<br />
c�����y was ��s�i�a���� as �h�� si�p���� av���a��� �f �h��<br />
��s� ����h���� a�� s���h���� ���a�i��s. F�� p�ac�ica��<br />
reasons �high� mountains were defined as areas<br />
wi�h h��i�h�s �f ����� �ha� 1000 � a.s.��.�� a���h���h<br />
the definition according to the Water Framework<br />
Di���c�iv�� a��� a���as a��v�� 800 �. F���h����� �h�� ���a��<br />
a���a �f ��a���s was ����h��y ��s�i�a���� f�� ��ach<br />
c�����y �y �����ip��yi�� �h�� s�-ca������� "�i��ici�y<br />
Index� (UNEP/DEWA 2005), defined as the<br />
p���c����a��� �f ���a�� f���shwa���� s��fac�� a���a�� wi�h<br />
�h�� ���a�� ��a�� a���a �f �h�� ���sp��c�iv�� c�����y.<br />
��a�is�ica�� a�a��ys��s �f �h�� �����a�i��ships ����w�����<br />
sp��ci��s �ich���ss a�� ������aphica�� pa�a�������s<br />
w����� ca��i��� ��� �si�� �h�� p����a���� ��TUTE<br />
(DDU Software 1993). The correlation between<br />
sp��ci��s �ich���ss a�� a���a �f�� ��ach c�����y �h��<br />
���a�� ������aphica�� a���a a�� ���a�� ��a��� a���a��� �h��<br />
so-called species – area relationship (SAR) was<br />
a�a��ys��� acc���i�� �� �h�� f��� � = c � �� �� wh����� �<br />
is sp��ci��s �ich���ss�� � is �h�� a���a�� a�� c a�� �� a���<br />
c��s�a��s ���.�. R�s�����w��i� 199��. Th�� f������a<br />
may be written as log S = log c + z log A, i.e. a<br />
��i���a� f��c�i�� �� a ����-���� sca����. This is a �������a��<br />
relationship found repeatedly among different<br />
groups of plants and animals, and at different<br />
sca����s ���.�. R�s�����w��i� 199��� �a��-J���s��� 2000�.<br />
O�h��� c�������a�i��s w����� ���s���� ���-pa�a�����ica����y<br />
��p��a��a� �a�� c�������a�i��� as �h�� ���sp��c�iv��<br />
�����a�i��ships w����� ��� ���p��c���� �� f������w a c����ai�<br />
�a�h���a�ica�� f������a.<br />
PRI�ER v���si�� � �PRI�ER-E ���. 2000�� s���� a��s�<br />
C��a���� & Wa�wic� 1994� was �s��� �� a�a��ys��<br />
si�i��a�i�i��s ����w����� �h�� fa��as �si�� B�ay-C���is<br />
si�i��a�i�y i����� �� p���s���c��/a�s���c�� �a�a.<br />
<strong>Ferrantia</strong> • 55 / 2008
P. Wiberg-Larsen Overall distributional patterns of European <strong>Trichoptera</strong><br />
Table 1: Species richness of <strong>Trichoptera</strong> and geographic characteristics of 26 European countries.<br />
Species that are only recorded from Mallorca, Corsica, Sardinia, Elba, Crete, and the Aegean<br />
Islands are excluded. Values for latitude are means (northern latitude + southern latitude/2).<br />
Country Area (km2 ) Latitude Species<br />
richness<br />
��s��ia ��� 83 8�0 47.2 302 �a��ic�y 1999<br />
B�����i�� �BE� 30 �13 �0.� 200 ������ 1987<br />
B����a�ia �BU� 110 912 42.� 239 K��a�s�i 1981�� 198��� 1988<br />
C����ch R��p����ic �CZ� 78 664 �0.0 247 Chv�j�a & N�va� 2001<br />
D����a�� �DK� 43 080 �6.0 169 Wi�����-�a�s��� 200� 1<br />
Results<br />
Th�� ��i�i�a�� �a�as��� i�c������� 976 sp��ci��s �cc���i��<br />
i� a� ����as� ���� �f �h�� 26 c�����i��s i� c��si����a�i��.<br />
After exclusion of island species from the lists of<br />
�h�� I����ia� P���i�s���a�� F�a�c���� I�a��y a�� G�����c�� �s����<br />
����h��s a�� �a����ia��s� �h�� �a�as��� was �����c��� ��<br />
891 sp��ci��s. Of �h��s�� 83.�% was ���si��a���� ����ic��<br />
16.2% ������ic a�� ����y 0.3% �������s��ia��.<br />
Th�� ��R f�� ����ic a�� ������ic sp��ci��s�� ���sp��c�iv����y��<br />
was v���y w��a� �� 2 =0.04/0.08) and not significant<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
References<br />
Es���ia �EE� 4� 100 �8.7 179 Vii�a����pp & Ti���� ��p����. 1<br />
Fi���a�� �FI� 337 032 64.6 212 �aas����� ��� a��. 1998 2<br />
F�a�c�� �FR� �38 300 46.3 393 Tach��� 200� 2��3<br />
G����a�y �DE� 3�6 829 �1.0 312 R������ 2001<br />
G�����c�� �GR� 118 300 37.0 231 �a��ic�y 1993�� 2004 3<br />
H���a�y �HU� 93 036 47.0 210 Uh�����vich & Nó��á�i 1999 2<br />
I����ia� P���i�s���a �IB� �88 700 40.0 361 G����a������ ��� a��. 1992 1��2��3 �� �a��ic�y 2004<br />
I�����a�� �IR� 70 283 143 Wa����ac�� ��� a��. 1990; E�i����� & Hi������w 199�<br />
I�a��y �IT�� 276 900 42.0 360 Cianficconi 2002 2��3<br />
�a�via ���� 63 700 �7 189 �p��is 1989<br />
����������� ��U� 2�86 49.8 183 ��s��� �a�i��a�� ��his��i��� �a������������� ����������� 200�<br />
N���h�����a��s �N�� 41 160 �2.2 17� Hi������ 199� 2<br />
N��way �N� 386 317 64.� 19� ������� & G�������f��s 1996 2<br />
P���a�� �P�� 312 683 �2.0 276 C��ach���ws�i 2002 2<br />
R��a�ia �RO� 237 �00 46.0 26� Ujva��si 1998 2��3<br />
����va�ia ���K� 49 03� 49.0 219 Chv�j�a & N�va� 2001<br />
����v���ia ���N� 20 2�� 46.0 224 K��s�i� & U��a�ic 2002 2<br />
�w������ ��E� 4�0 089 62.3 220 G�������f��s 2002 2<br />
�wi��������a�� ��CH� 41 293 314 ���i�a-F�����i� & Vic����i�i 200� 3<br />
U�i���� Ki����� �UK� 244 102 197 Wa����ac�� 1991<br />
Remarks:<br />
1 ��pp������������ �y ��p����ish��� ���c���s<br />
2 ��pp������������ �y ���c���� p����ish��� ���c���s<br />
3 C�����c�i��s acc���i�� �� �a��ic�y 200�<br />
�P=0.10/0.19� f�� �h�� 24 c�����i��s c��si������� �� �h��<br />
European continent (Fig. 1). However, a significant<br />
p�si�iv�� �����a�i��ship was f���� ����w����� �h��<br />
������� �f ������ic sp��ci��s a�� ��a��� a���a �� 2 =0.34��<br />
P
P. Wiberg-Larsen Overall distributional patterns of European <strong>Trichoptera</strong><br />
146<br />
Species richness<br />
1000<br />
100<br />
10<br />
1<br />
Slot= 45.8A 0.11<br />
r 2 = 0.08, N.S.<br />
Slen = 33.1A 0.04<br />
r 2 = 0.04, N.S.<br />
1000 10000 100000 1000000<br />
Area (km 2 )<br />
lotic species<br />
lentic species<br />
Fig. 1: The relationship between species richness of <strong>Trichoptera</strong> and geographic area for 24 countries on the<br />
European continent. Analyses are carried for lotic and lentic species, respectively.<br />
Species richness<br />
1000<br />
100<br />
10<br />
1<br />
S = 43.9LA 0.08<br />
r 2 = 0.34, P
P. Wiberg-Larsen Overall distributional patterns of European <strong>Trichoptera</strong><br />
Species richness<br />
350<br />
300<br />
250<br />
200<br />
150<br />
100<br />
50<br />
0<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
rs(lot)=-0.79<br />
P
P. Wiberg-Larsen Overall distributional patterns of European <strong>Trichoptera</strong><br />
148<br />
Species richness<br />
350<br />
300<br />
250<br />
200<br />
150<br />
100<br />
50<br />
0<br />
lotic species<br />
lentic species<br />
endemic species<br />
rs(lot)=0.70<br />
p 1000 m a.s.l<br />
rs(end)=0.80<br />
p
P. Wiberg-Larsen Overall distributional patterns of European <strong>Trichoptera</strong><br />
was p�si�iv����y c�������a���� wi�h �h�� �ich���ss �f ����ic<br />
sp��ci��s �� s =0.7��� P
P. Wiberg-Larsen Overall distributional patterns of European <strong>Trichoptera</strong><br />
150<br />
the area of �high mountains� (in case defined as<br />
a���i�����s a��v�� 1000 � a.s.��.� a�� �h�����f���� �ay<br />
��� ���p���� �� "hi�h" ����p���a�����s�� ��v��� �h���h<br />
several species may be confined to valleys rather<br />
�ha� �� ha�i�a�s a� hi�h��� a���i�����s. ������v�����<br />
�h�� ����ic fa��as �f �����ai�-�ich c�����i��s i�<br />
central and southern Europe are very different,<br />
��sp��cia����y i� �h�� ��s� s���h���� pa��. This i��ica���<br />
a� ���p��a�a�i�� �����a���� �� �h�� ����� p���i��s wi�h���<br />
���acia�i��s �ha� �his pa�� �f E���p�� has ���p���i���c���<br />
c��pa���� �� ����h���� E���p���� �� �h�� p�ssi�i��i�y �f<br />
a ����� p������c��� ���ca�� is���a�i�� i� �����ai���s<br />
a���as �ha� a��s� s�pp���s a ��a���� va�i���y �f s����a�<br />
ha�i�a�s�� a�� �� �h�� �����a�iv�� is���a�i�� �f �h�� I����ia���<br />
I�a��ia��� a�� G������ p���i�s���a. �a��ic�y �1983��<br />
1988, 2000) defined a zoogeographic biome type<br />
f�� ����ic T�ich�p����a�� �h�� "DINOD��" �i.��. "aq�a<br />
�����������a"� a�� s�����s���� �ha� sp��ci��s �ich���ss �f<br />
�h��s�� was hi�h��s� i� �����ai�s �f C�����a�� E���p��<br />
a�� Ba���a�. �a��ic�y �1988�� 2000� f���h��� a������<br />
�ha� �h�� �aj��i�y �f DINOD�� T�ich�p����a has<br />
�����a�iv����y s�a���� �is��i���i��a�� a���as a�� �ha� �h��s��<br />
p���s�����ay a���as �����a��� �� ���f��ia wh����� ����a���<br />
sp��ci��s s��viv��� ��fav���a����� ���acia�i�� p���i��s<br />
���.�. i� p���iph���a�� hi�h��a��s�. This hyp��h��sis has<br />
���c������y ���c��iv��� s���i� s�pp��� �y Pa���s �2004�<br />
wh� s���i��� �h�� �������ic s���c����� �f E���p��a�<br />
p�p���a�i��s �f Drusus discolor �Ra���� 1842�.<br />
Thus, the differentiation between presentday<br />
p�p���a�i��s �f D. discolor �ay hav�� ������ a ���s����<br />
�f �������a� i��� �����ip���� i����p�������� P����is��c�����<br />
���f��ia a�� ��i���a��� �iv�������c�� ���i�� p���i��s<br />
�f is���a�i��. F���h����� Pa���s �2004� s�����s�s �ha�<br />
�h��s�� p��c��ss��s a��� a�a������s �� �h�s�� �ha� hav��<br />
����� �� hi�h sp��ci��s �iv���si�y a�� ��a���� ������� �f<br />
���ca�� �������ics�� �h������y s�pp���i�� �h�� i���a �ha�<br />
�������a� i��� ���acia�� ���f��ia ca� p������� sp��cia�i��.<br />
H�w��v����� �h�� s���y �y Pa���s �2004� a��s� p�i��s a�<br />
a ����� ���c���� sp��cia�i�� a���� ����ic E���p��a�<br />
T�ich�p����a.<br />
�y s���y i������� i��ica���s �ha� �is��i���i��a��<br />
a���as �f ����ic T�ich�p����a a��� i� �������a�� �����a�iv����y<br />
s�a���� as 6� % �f �h��s�� sp��ci��s w����� f���� i� j�s�<br />
1-3 c�����i��s/����i��s�� wh�����as �his is ����y �h�� cas��<br />
f�� 2� % �f �h�� ������ic sp��ci��s �f which ����� �ha�<br />
ha��f a��� wi�����y �is��i������ �i.��. f���� i� �����<br />
�ha� 1� c�����i��s/����i��s�. ������v��� acc���i�� ��<br />
�h�� p���s���� s���y�� 42 % �f �h�� c���i�����a�� I����ia�<br />
fa��a�� 28 % �f �h�� c���i�����a�� G������ fa��a�� a�� 19<br />
% �f �h�� c���i�����a�� I�a��ia� fa��a �ay ��� ����a�����<br />
as �������ics. �c��a����y �h�� ��������� �f �������is� is<br />
��v��� hi�h��� if �h�� ��������s s��sp��ci��s �ha� �cc��<br />
i� ��.�. �h�� I����ia� P���i�s���a a�� ��sp��cia����y I�a��y a���<br />
taken into consideration (see Cianficconi, Moretti<br />
& T�ccia�������i 1997�. This w����� a��s� hav�� ���s�������<br />
in even greater differences between the faunas in<br />
Fi�. 6�� p�i�a�i��y i� �h�� s���h���� pa�� �f E���p��.<br />
B���sa���a�� �197�� c��vi�ci����y ���sc�i���� �h��<br />
isolation influence of mountains on endemism.<br />
Th�s�� a� ����as� 42 sp��ci��s �� s��sp��ci��s a���<br />
�������ic �� �h�� Ca�pa�hia� �a������ ���p���s����i��<br />
a���� 1� % �f �h�� wh����� Ca�pa�hia� T�ich�p����a<br />
fa��a. Th�� c��si����a����� �������h �f �h�� Ca�pa�hia�<br />
�a������ i�s s���ivisi�� �y ��a�sv���s�� va������ys a��<br />
i���a����a��� ���p���ssi��s�� a�� i�s f��c�i�� as a<br />
�i�������aphica�� c��ssway �ay hav�� p��������<br />
�his hi�h ��������� �f �������is�. This is s�pp������ �y<br />
studies of a Rocky Mountain stonefly, showing that<br />
steep mountain walls may act as effective barriers<br />
of dispersal increasing the genetic differentiation<br />
i� a�jac���� ��� y��� is���a���� p�p���a�i��s �H��h��s��<br />
�a�h����� �h������� & �����������f 1999�. I� a��i�i����<br />
i� is ������s��a���� �ha� ���a�is�s wi�h ��i�i����<br />
�isp���sa�� capaci�y a��� �����a�iv����y �ich i� �������ics<br />
���.�. �a��-J���s��� 2000�. E�����ic sp��ci��s a���<br />
��sp��cia����y a����a�� a���� �h�� fa�i��i��s B���a��i�a����<br />
G���ss�s��a�i�a���� Hy���p�i��i�a���� Phi���p��a�i�a����<br />
Psych��yii�a���� Rhyac�phi��i�a���� a�� �h��<br />
s��fa�i��y D��si�a�� ��i����phi��i�a����� a���� ���i��<br />
obligate or predominantly confined to different<br />
�yp��s �f ����i�� wa����s. Th����� a��� i��ica�i��s<br />
�ha� ��������s �f a� ����as� s���� �f �h��s�� ����ps<br />
�ay hav�� a �a�h��� ��i�i���� �isp���sa�� capaci�y ���.�.<br />
����� & Wi�����-�a�s��� 1993; C�����i��� & ��i�h 1998;<br />
Pa���s 2004� c��pa���� wi�h ������ic sp��ci��s �f ��.�.<br />
Ph�y�a���i�a�� a�� c����ai� ��i����phi��i� �������a ���.�.<br />
�v���ss�� 1972�� 1974; Wi�����-�a�s��� & Ka�sh����<br />
1999�. �i�i���� �isp���sa�� capaci�i��s c���i���� wi�h<br />
a ��a���� a���a wi�h��� �����ai�s �ay a��s� ���p��ai�<br />
why �a�y ����ic T�ich�p����a i�ha�i�i�� �h�� C�����a��<br />
E���p��a� �����ai�s hav�� ������ ��a����� �� c�����i����<br />
s�i�a����� ha�i�a�s i� �h�� �ca��i�avia� �����ai�s<br />
f������wi�� �h�� ��a���s� ������acia�i��.<br />
The difference in distributional patterns between<br />
����ic a�� ������ic T�ich�p����a �ay �� s���� �������� ���<br />
���p��ai���� �y a �������a����y hi�h��� �������a�c�� ��wa��s<br />
wi��� ����p���a����� a�p��i�����s a���� sp��ci��s<br />
�cc�pyi�� ��a���s a�� p���s. Th�s�� �h�� ����p���a�����<br />
�a���� �f p���s a�� ��a���s �ay ��� c��si����a�����<br />
c��pa���� wi�h �ha� �f ������wa���� f��� s����a�s a��<br />
�����ai���s s����a�s. I� a��i�i���� �pp�����is�ic<br />
a�� v���y ���i���� sp��ci��s �ha� �ay hav�� c�p���<br />
w������ wi�h �h�� ���acia�� p���i��s a��� ����� a����a��<br />
<strong>Ferrantia</strong> • 55 / 2008
P. Wiberg-Larsen Overall distributional patterns of European <strong>Trichoptera</strong><br />
i� ������ic �ha� i� ����ic ���vi��������s ��a��-J���s���<br />
2000�. G������a����y�� �his �ay i�p��y a �����a�iv����y wi����<br />
������aphic �is��i���i�� a���� ������ic sp��ci��s<br />
�ha� a���� ����ic sp��ci��s a�� �h�����f���� a ����a����<br />
si�i��a�i�y �v��� ��a����� ������aphica�� a���as. Th�s�� �h��<br />
hi�h �ich���ss �f ������ic sp��ci��s i� ����h���� E���p��<br />
c����� ��� ���p��ai���� �y �i��a�i�� f��� P����is��c�����<br />
���f����s s����wh����� i� �h�� Eas� �h����h �h�� p��ai�s<br />
of Russia (Malicky, in litt.). And some of these<br />
sp��ci��s �ay ��� hav�� a��iv��� �� s���h���� E���p��<br />
y���. H�w��v����� a s��ai�h� f��wa�� ���p��a�a�i�� is<br />
�����a���� �� �h�� p���s�����ay hi�h a����a�c�� a��<br />
a���a �f ��a���s a�� p���s i� ����h���� E���p�� �����<br />
�� �h�� ���acia�i��s �ha� c���a���� �a�y ��a���s�� s����<br />
�a��-J���s��� 2000� as sh�w� �y �y a�a��ys��s��<br />
�� �h�� hi�h �iv���si�y �f �h�� ��a���s a�� p���s i�<br />
����h���� E���p���� a�� �� �h�� p������i�a�c�� �f<br />
������ic ��i����phi��i� a�� ph�y�a���i� sp��ci��s �ha�<br />
���p���i� �h��s�� ha�i�a�s. Th�s�� �h��s�� �w� fa�i��i��s<br />
c��s�i����� �p �� 60 % �f �h�� ���a�� ������ic T�ich�p����a<br />
fa��a�� a�� �a�y �f �h��i� ���p���s����a�iv��s �cc��<br />
only in specific lentic habitats. The hypothesis<br />
�ay ��� pa����y s�pp������ �y a s���y �f hi�h<br />
a���i����� N���h-�����ica� w�����a��s �ha� �ay ���<br />
c��pa�a����� �� �h�� ����h E���p��a� w�����a��s��<br />
sh�wi�� �ha� �h�� �is��i���i�� �f ��i����phi��i� a��<br />
ph�y�a���i� sp��ci��s ���p����s �� a p���vai��i�� ��a����<br />
permanence gradient and, thus, on many different<br />
ha�i�a�s �Wissi������� B��w� & Ja���� 2003�.<br />
Th�� fa��a �f �h�� UK a�� Th�� N���h�����a��s a���<br />
�a�h��� si�i��a�. This �ay ��� ��� a s��p�is�� as<br />
E����a�� was c�����c���� wi�h �h�� E���p��a�<br />
Continent until about 7000 – 8000 calender years<br />
BP. Pa��a�����i�������ica�� s���i��s �f s���i�����s i� �h��<br />
River Trent floodplain have shown that this river<br />
ha� a����s� �h�� sa��� T�ich�p����a fa��a app���. 13<br />
000 ca��. y��a�s BP as i� has ��wa�ays �G������w�����<br />
�����w & W��� �2003�. ������v����� Micrasema<br />
setiferum ��c�ach��a� 1876� a�� Brachycentrus<br />
maculatum �F���c��y 178���� �ha� �� ��� �cc�� �� �h��<br />
B�i�ish Is����s ��wa�ays ��� a��� wi�����y �is��i������<br />
�� �h�� c���i������� w����� f���� as s��f�ssi��s i� �h��<br />
River Trent floodplain sediments (Greenwood,<br />
�����w & W��� 2003; G������w����� W��� & ������<br />
i� p���ss�. This i�p��i��s �ha� c�����isa�i�� �y ���w��a��<br />
sp��ci��s f��� �h�� s���h ��s� hav�� ������ �����a�iv����y<br />
fas� f������wi�� �h�� ��a���s� ������acia�i��; s���� a��s�<br />
Wi�����-�a�s����� B����i����� J���s��� & ������� �2001�<br />
wh� f���� a� a����s� p���s�����ay T�ich�p����a<br />
ass������a��� i� 10��300 ca��. y��a�s ���� �iv��� s���i�����s<br />
i� �h�� G���a� B����� �D����a���.<br />
<strong>Ferrantia</strong> • 55 / 2008<br />
I�����a�� was ��i����� �� E����a�� ���i�� a���� 12 000<br />
– 8000 cal. years ago and, thus, it was before that<br />
�i��� a��s� a pa�� �f �h�� c���i�����. H�w��v����� ���i��<br />
s��pa�a���� f��� �h�� c���i����� f�� a �������� �i���<br />
�ha� E����a���� I�����a�� �������a����y has a s����wha�<br />
poorer flora and fauna – including <strong>Trichoptera</strong> -<br />
�ha� E����a��.<br />
Th�� �s�� �f I����i��s�s ���c�����i��s� i�s���a� �f c�����y<br />
�������s w����� hav�� ������ �h�� �a���a�� ����p��a���<br />
analysing the overall distributional pattern<br />
�f E���p��a� T�ich�p����a i� �h�� p���s���� s���y.<br />
H�w��v����� a� �p �� �a��� ���visi�� �f �h�� ch��c���is� �y<br />
B���sa���a�� & �a��ic�y �1978� was ��� avai��a�����.<br />
N��v����h������ss�� �h�� �s�� �f c�����y ch��c���is�s �ay<br />
i� s���� pa��s �f E���p�� ��� p���f���a����� c��pa����<br />
wi�h ��c�����i��a�� ��is�s. Th�s�� �h�� si�i��a�i�y a�a��ysis<br />
showed remarkably large differences between the<br />
fa��as �f D����a�� a�� �h�� N���h�����a��s �ha� ���h<br />
�������� �� ��c�����i�� 14. This is a��s� �h�� cas�� f�� �h��<br />
fa��a �f �h�� ���s� �f �his ��c�����i�� �ha� i�c������s<br />
�h�� ����h���� ���w��a�� �f G����a�y a�� P���a��<br />
�a�a��ys��s ��� sh�w� h������.<br />
Th�� p���s���� s���y has c����a���y f�c�ss��� �� �h��<br />
�is��i���i�� �f E���p��a� T�ich�p����a �� a�<br />
a�s���������y ��a���� sca������ a�� �h�� c��c���si��s ��aw�<br />
��s� �h�����f���� ��� p�����i�i�a�y. H�w��v����� �h��<br />
a�a��ys��s �s��� i� �h�� s���y hav�� c����ai���y sh�w�<br />
�h��i� p������ia�� a�� �ay ��� app��i��� �� �a�as���<br />
describing the distribution of caddisflies in much<br />
����� ����ai���� ��.�. �h�� v���y �iv���s�� a�� ����i��a����y<br />
varied Italian Fauna (see Cian���coni, Moretti &<br />
T�ccia�������i 1997�. ��ch a�a��ys��s �si�� �a�a f���<br />
80 p��vi�c��s i� F�����sca��ia a�� D����a�� �ay<br />
sh�w i�������s�i�� ���s����s �G�������f��s�� �a����a������ &<br />
Wi�����-�a�s����� i� p���p.�.<br />
Acknowledgements<br />
� p�����i�i�a�y v���si�� �f �h�� p���s���� s���y was<br />
i�c������� i� �y PhD �h��sis �Wi�����-�a�s��� 2004�. I<br />
a� ��s� ��a���f��� �� P��f��ss�� D�. Ha�s �a��ic�y a��<br />
P��f��ss�� Kaj �a��-J���s��� f�� �h��i� c��s���c�iv��<br />
c�i�icis� a�� s�����s�i��s ����a��i�� �h�� PhD �h��sis<br />
�ha� i�spi���� ��� �� ���vis�� �h�� ��i�i�a�� �a�as��� as<br />
w������ as �h�� a�a��ys��s �s��� i� �ha� �h��sis. I a��s� wish<br />
�� �ha�� �y c�������a����s D�. �a�c�s G����a�������� B�<br />
G�������f��s�� J�ha �a����a�������� D�. D�����s �ch����a��<br />
Dr. Henn Timm, and Dr. Gorarzd Urbanič for their<br />
h����p i� p��vi�i�� fa��is�ics �a�a.<br />
151
P. Wiberg-Larsen Overall distributional patterns of European <strong>Trichoptera</strong><br />
152<br />
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��i�h �2001��� ��i�h �2001�� 2002��� ���i�h 2001��� ���i�h<br />
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Hø��� J. T. & �ü������ J. 198�. - C��pa�a�iv�� ���ph�����y<br />
and phylogeny of the family Thompsoniidae (Cirripedia:<br />
Rhizocephala: Akentrogonida) with description of three<br />
new genera and seven new species. Zoologica Scripta 22:<br />
363-386.<br />
Marshall C. R. 1987. - Lungfish: phylogeny and<br />
pa�si���y�� i� B����is W. E.�� B�������� W. W. & K���p<br />
N. E. (eds), The Biology and Evolution of Lungfishes,<br />
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Röc����� D.�� K��� W. & K�h� �. J. 199�. - �a��a�� �f �h��<br />
Living Conidae. Volume 1: Indo-Pacific Region. Christa<br />
H��������� Wi��s�a������ �17 p.<br />
�chwa���� T. D. 198�. - P�p���a�i�� s���c����� �f ���ac� �i����<br />
snakes, Notechis ater niger, on off-shore islands of South<br />
Australia: 35-46, in Grigg G., Shine R. & Ehmann H.<br />
����s��� Bi�����y �f ��s��a��asia� F���s a�� R��p�i����s. ������y<br />
Beatty and Sons, Sydney.<br />
Gerecke R. et al. 2005. - Die Fauna der Quellen und<br />
���s hyp��h��isch��� I�����s�i�ia��s i� ���������� ������<br />
���s��������� B���üc�sich�i���� ���� �i������ ��ca�i���<br />
��sch���������s�� �Os��ac��a� ��� R�����f�ss�����s��<br />
�C�p��p��a�. F����a��ia 41�� ��s��� �a�i��a�� ��his��i���<br />
�a������������� ������������� 140 p.<br />
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LISTE DES NUMÉROS PARUS À CETTE DATE<br />
Travaux scientifiques du Musée national<br />
d'histoire naturelle (1981-1999)<br />
I ����as p��vis�i��� ���s I�s��c���s �� G�a��-D�ch�<br />
��� �����������. ���pi��p����a. 1 �� pa��i��<br />
�Rh�pa���c���a�� H��sp���ii�a���. �a�c ���y��� ���<br />
���ph��s�� P��������s�� 1981.<br />
II N��v��������s ������s pa�����������iq���s ���<br />
�i�s��a�i��aphiq���s s�� ����s �����i���s ��<br />
G�a��-D�ch� ��� ������������� ��� ��a P��vi�c��<br />
�� ����������� ��� ��� ��a ���i�� ����ai���<br />
attenante. Pierre L. Maubeuge, 1984.<br />
III R��visi�� �f �h�� ���c���� W��s����� E���p�� sp��ci��s<br />
�f �����s Potamocypris �C��s�ac��a�� Os��ac��a�.<br />
Part 1: Species with short swimming setae on<br />
�h�� s��c��� a������a��. C��a���� ���isch�� 1984.<br />
IV H�����p���s �� G�a��-D�ch� ��� �����������<br />
1. Psallus (Hylopsallus) pseudoplatani �. sp.<br />
��i�i�a���� Phy��i�a��� ��� ��spèc��s appa��������s.<br />
���p���� R��ich��i���� 1984.<br />
2. Quelques esp�ces peu connues, rares ou<br />
inattendues. Léopold Reichling, 1985.<br />
V La bryoflore du Grand-Duché de Luxembourg:<br />
�a���s ���v��a���� �a���s �� ��c����s. Ph. D��<br />
Zuttere, J. Werner et R. Schumacker, 1985.<br />
VI R��visi�� �f �h�� ���c���� W��s����� E���p�� sp��ci��s<br />
�f �����s Potamocypris �C��s�ac��a�� Os��ac��a�.<br />
Part 2: Species with long swimming setae on<br />
�h�� s��c��� a������a��. C��a���� ���isch�� 198�.<br />
VII ���s B�y����ai���s �� G�a��-D�ch� ���<br />
����������� ��� ���s ���i��s ��i�i���ph��s.<br />
Ga�y G��i���� ��� J�s. �assa���� 1986.<br />
VIII R�pa��i�i�� ��� �c�����i�� ���s �ac����ich���s<br />
�piphy�iq���s �a�s ���� G�a��-D�ch� ���<br />
�����������. E��isa����h Wa�����-�cha������<br />
1987.<br />
IX La limite nord-orientale de l�aire de<br />
Conopodium majus �G��a�� ������ ��� E���p��<br />
�cci�����a����. R��i��� Fa��i�� 1987.<br />
X Epifaune et endofaune de Liogryphaea arcuata<br />
��a�a�c��. C����i���i�� à ����c�����i�� ���s<br />
p�p���a�i��s ��� Liogryphaea arcuata ��a�a�c��<br />
�a�s ���� �i�����i��� a� NE �� Bassi� ��� Pa�is.<br />
���a�� Ha�y�� 1987.<br />
XI Liste rouge des Bryophytes du Grand-Duché<br />
��� �����������. J��a� W��������� 1987.<br />
XII Relic stratified scress occurences in the<br />
O��s��i�� �G�a��-D�chy �f ��������������<br />
app���i�a��� a��� a�� s���� fa��ic p��p����i��s.<br />
P������ �. Ri��������s�� 1987.<br />
XIII Die Gastropodenfauna der «angulata-Zone�<br />
des Steinbruchs «Reckingerwald� bei Brouch.<br />
H��������� ���i��� ��� K��� ���i���s�� 1988.<br />
XIV ���s ��ich���s �piphy�iq���s ��� ������s cha�pi����s<br />
��ich��ic�����s ��ac����ich���s ���c��p��s� ��<br />
�����������. Pa��� Di������ich�� 1989.<br />
XV Liste annotée des Ostracodes actuels non-<br />
�a�i�s ����v�s ��� F�a�c�� �C��s�ac��a��<br />
Os��ac��a�. C��a���� ���isch�� Ka����� W������s ���<br />
K���� �a�����s�� 1989.<br />
XVI Atlas des lichens épiphytiques et de leurs<br />
cha�pi����s ��ich��ic�����s ��ac����ich���s<br />
���c��p��s� �� �����������. Pa��� Di������ich��<br />
1990.<br />
XVII B��i��a� ���� Fa��is�i� ��� ������i�� ����<br />
Schmetterlinge im ehemaligen Erzabbau-<br />
����i��� "Haa���" ���i Dü�����i�����. J�s. C���s��<br />
1991.<br />
XVIII Moosflora und -Vegetation der Mesobrometen<br />
ü���� ����i��������������p��� i� �������������<br />
��� i� Bi�������� G����a��. J��a� W��������� 1992<br />
19 Os��ac��a. Nic� W. B�����a������� K����<br />
�a�����s�� C��a���� ���isch�� T�aja� K. P�����vs�i<br />
a�� Ka����� W������s�� 1993.<br />
20 ���s hai��s a� G�a��-D�ch� ��� �����������.<br />
K��j��v D��s��������� Di�i��� D����a���� �a�c<br />
����s�� C��a��i� Wa����������� 1993.<br />
21 Ec�����y a�� V������a�i�� �f �� T�i���a�� N��w<br />
G�i���a �I�ia� Jaya / I������sia�. J��a�-�a�i��<br />
�a������� 1993.<br />
22 � ch��c���is� �f �h�� ���c���� ���-�a�i��� �s��ac��s<br />
�C��s�ac��a�� Os��ac��a� f��� �h�� i���a�� wa����s<br />
�f ����h �����ica a�� a�jac���� is��a��s. K����<br />
�a�����s & F�a�cis B��h����� 1993.<br />
23 Os��ac��a. C��a���� ���isch�� R���a�� F�h��a����<br />
Ka����� W������s�� Ga��i������ B��y��� a�� T�aja�<br />
P�����vs�i�� 1996.<br />
24 Die Moosflora des Luxemburger Oeslings.<br />
J��a� W��������� 1996.<br />
2� ����as ���s p���i��phy���s ���s ���i��s �����ai���s<br />
��� v�s�i������s�� av��c ����s �����i��i���s a�jac����s��<br />
G�������s H����i Pa������� 1997.<br />
26 Eva���a�i�� ��� ��a q�a��i�� ���s c���s ����a� a�<br />
����������� ��� �a�� q��ha�i�a� p��� ��a ��������.<br />
G���p�� ������� ������������� 1997.<br />
27 N����s Pa�����������iq���s ��� Bi�s��a�i��aphiq���s<br />
s�� ���� G�a�� D�ch� ��� ����������� ��� ����s<br />
���i��s v�isi���s. Pi������ ���is �a�������� &<br />
D��i�iq��� D����sa����� 1997.<br />
28 Die Moosflora der Kleinen Luxemburger<br />
�chw��i�� ��ü��������a���. F����ia� Ha�s�� 1998.
29 E����� s�� ����s �������s Globorilusopsis �a����������<br />
1994 ��� Simoniceras �. ����. �� �ias ��p��i���� ��<br />
G�a��-D�ch� ��� ����������� �Ca��yp��p���a�i-<br />
�a�. Pi������ ���is �a���������� 1998.<br />
30 ��Ich�hy�fa���� �� T�a�ci��� ���������������is.<br />
Ca���� �����a�� ��� ca�a������� s�a�is�iq���.<br />
D��i�iq��� D����sa����� 1999.<br />
31 P��c�����i��s �f �h�� 3�� E���p��a� Ba�������c���<br />
Workshop. 16-20 August 1996 Larochette (Lux.).<br />
Ch�is�i��� Ha���sch & Jacq���s Pi� ����s.���<br />
1999.<br />
32 ���s c�������c�i��s pa�����������iq���s �� ��s���<br />
�a�i��a�� ��his��i��� �a����������� ��� �����������.<br />
F�ssi����s �� T�ias ��� �� J��assiq���. D��i�iq���<br />
Delsate, Chris Du���n & Robi Weis, 1999.<br />
FERRANTIA (2002- )<br />
33 Die Fledermäuse Luxemburgs (Mammalia :<br />
Chi��p����a�. Ch�is�i��� Ha���sch�� E�����<br />
E�������� Jacq���s Pi��� 2002.<br />
34 Th�� P�����a �f �����������. ��������j<br />
�����p�yc�i�� N������� ����p�� Wa��a �. W��i������<br />
2003.<br />
3� �is��� ������ ���s ��y�phy���s �� �����������.<br />
J��a� W��������� 2003.<br />
36 Pa�����������i�� a� �����������. �i�����<br />
Guérin-Franiatte (éd.), 2003.<br />
37 V�������i����sa���as ���� ��phi�i��� ���s<br />
G��ßh����������s ����������. R���a�� P����ss<br />
���.��� 2003.<br />
38 T��is ������s s�� ��a Z���� R����� ��� V������.<br />
I. Herpétofaune. II. La diversité floristique.<br />
III. ���s si���s ��i����ê� ���a�iq��� ��� ��������iq���.<br />
G�������s H. Pa������� 2004.<br />
39 V�������i����sa���as ���� H���sch���c���� ���s<br />
G��ß-h����������s ����������. R���a��<br />
P����ss�� 2004.<br />
40 ���s �ac����ich���s ��� B�����iq����� ��<br />
����������� ��� �� ���� ��� ��a F�a�c�� - C���s<br />
��� �������i�a�i��. E. ����sia���� P. Di������ich<br />
& J. �a��i����� 2004.<br />
41 Die Fauna der Quellen und des<br />
hyp��h��isch��� I�����s�i�ia��s i� ����������<br />
������ ���s��������� B���üc�sich�i���� ����<br />
�i������ ��ca�i��� ��sch���������s�� �Os��ac��a�<br />
��� R�����f�ss�����s�� �C�p��p��a�. R��i�ha��<br />
G�����c����� Fa�i� ���ch�� C��a���� ���isch�� Isa�����<br />
�ch�a�������� 200�.<br />
42 R��� �is� �f �h�� Vasc���a� P��a��s �f �����������.<br />
G�y C�����i���� 200�.<br />
43 C����i���i�� à ��a c��i�a������i�� ��<br />
�����������. ��a��ys��s his���iq���s�� sc��a�i�s<br />
f����s. Ch�is�ia� Ri��s ���.��� 200�.<br />
44 �a��s����� �a��scap��s i� E���p�� - Pas���<br />
P���s���� a�� F������. P��c�����i��s �f �h�� 2��<br />
I������a�i��a�� C��f������c�� �� �a��s�����<br />
�a��scap��s. Via����� ������������� 2�-<br />
28.0�.200�. Ch�is�ia� Ri��s & Yv��s K�ipp����<br />
�E�i���s��� 200�.<br />
4� ���i�i��s ��� c�����c�i��s a� ca�a������� ���s<br />
p��a����s vasc���ai���s ��� ���a�����iss������� ���<br />
�������y. E����� s�� ����v�����i�� s�c���ai��� ���<br />
la flore. Georges H. Parent, 2006.<br />
46 B��i���� ���� Pa���������i�� ���s U��������v��s<br />
����������s �1�. Ch�is�ia� F�a���� �H�s�.���<br />
2006.<br />
47 V�������i����sa���as ���� �i���������� ���s<br />
G��ßh����������s ����������. R���a�� P����ss��<br />
2006.<br />
48 ���s H���s ����i����a��s�� Fagus sylvatica �. va�.<br />
tortuosa P�pi��� ��� ����ai����� �a�s ������ c���������<br />
�����p����. G�������s H. Pa������� 2006.<br />
49 I�v����ai��� �i���a����iq��� �� ����������� -<br />
����������������� �chi�pach�� G���s���f. �i���<br />
Phi��ipp� ���.��� 2007.<br />
�0 I�v����ai��� ��� ��a �i��iv���si�� �a�s ��a f��ê�<br />
"�ch�����������" �C������� ��� B������f� -<br />
E�fass��� ���� Bi��iv���si�ä� i� Wa�������i���<br />
"�ch�����������" �G�����i���� B������f�. �a�c ���y���<br />
& Ev����y��� Ca��i��s ���s.��� 2007.<br />
51 Proceedings of the first international Recorder<br />
c��f������c��. ����������� 2-3 D��c������� 200�.<br />
Ta�ia Wa��isch �E�i������ 2007.<br />
�2 V�������i����sa���as ���� R��p�i��i��� ���s G��ßh����������s<br />
����������. R���a�� P����ss ���.���<br />
2007.<br />
�3 ���s a�����s i������i�s a� �����������.<br />
I�v����ai��� ���s ��ss���c��s a������sc������s ���<br />
i��i���s ��� p����i���������� p��s������s s�� ����<br />
�����i��i��� �� G�a��-D�ch� ��� �����������.<br />
�. W���������� J. T����� J. T��ss����� 2008.<br />
54 Fossils as Drugs: pharmaceutical<br />
palaeontology. Christopher J. Du���n, 2008.<br />
55 Proceedings of the first conference on<br />
fa��is�ics a�� ����������aphy �f E���p��a�<br />
T�ich�p����a. ����������� 2 �� - 4 �h ���p��������<br />
200�. �. ���y��� & P. N��� ����s.��� 2008.<br />
���s v�������s ��� ��a s���i����FERR�NTI��� pa�aiss����<br />
à i�����va������s ��� ������i���s.<br />
E�v�y���� v����� c���a���� a�� a����ss��s i��iq����s<br />
à ��a pa��� 2 ��� ��a c��v��������.