Chapter 1 - Núria BONADA

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Local scale: Optimums and tolerances in Trichoptera MACKAY, R. J. (1979). Life history patterns of some species of Hydropsyche (Trichoptera: Hydropsychidae) in southern Otario. Can. J. Zool., 57: 963-975. MALICKY, H. (1981). Der Indikatorwert von Köcherfliegen (Trichoptera) in groβen Flüssen. Mitt. Dtsch. Ges. Allg. Angew. Ent., 3: 135-137. MARCHANT, R. 1990. Robustness of classification and ordination techniques applied to macroinvertebrate communities from the La Trobe River, Victoria. Aust. J. Mar. Freshwat. Res., 41: 493-504. MOLI NA, C.; VIDAL-ABARCA, M. R. & SUÁREZ, M. L. (1994). Floods in arid south-east Spanish areas: a historical and environmental review. In: Rossi, G. (ed.). Coping with Floods. Kluwer Academic Publishers. The Netherlands: 271-278. MOLLES, M. C. (1982). Trichopteran communities of streams associated with aspen and conifer forest: long-term structural change. Ecology, 63: 1-6. MOOG , O. & CHOVAREC, A. (2000). Assessing the ecological integrity of rivers: walking the line among ecological, political and administrative interests. Hydrobiologia, 422/423: 99-109. MORETTI, G. P. & MEARELLI, M. (1981). Ecological profiles in three Rhyacophila species. Proc. 3 ua, 175: 20-37. PRAT, SOLÀ, C., & BONADA, N. (1999). La qualitat ecològica rivers and streams. Diputació de pp. RESH th ROBL RDO, I.; PRAT, N.; era) in a southern Appalachian stream system (USA). RUTT 81: 217-228. SMITH, M. J.; KAY, W. R.; EDWARD, D. H. D.; PAPAS, P. J.; RICHARDSONS, K. ST J.; an rivers. rd int. symp. Trichoptera: 227-230. MUNNÉ, A., SOLÀ, C., y PRAT, N. (1998). QBR: Un índice rápido para la evaluación de la calidad de los ecosistemas de ribera. Tecnología del Ag PETERSEN, L. B. M. & PETERSEN, R. C. Jr. (1983). Anomalies in Hydropsychid capture nets from polluted streams. Freswat. Biol., 13: 185-191. PRAT, N. 1993. El futuro de los ríos españoles: secos o contaminados. Quercus. Febrero: 22-24. N.; RIERADEVALL, M.; MUNNÉ, A.; del Llobregat, el Besòs i el Foix. Informe 1997. Diputació de Barcelona. Àrea de Medi Ambient (Estudis de la Qualitat Ecològica dels Rius, 6). 154 pp. PRAT, N., MUNNÉ, A., RIERADEVALL, M. SOLÀ, C. & BONADA, N. 2000. ECOSTRIMED: Protocol to stablish the ecological status of Mediterranean Barcelona. Àrea de Medi Ambient (Estudis de la Qualitat Ecològica dels Rius, 8). 94 pp. PRAT, N.; RIERADEVALL, M.; MUNNÉ, A.; SOLÀ, C., & BONADA, N. (2001). La qualitat ecològica del Llobregat, el Besòs, el Foix i la Tordera. Informe 1991. Diputació de Barcelona. Àrea de Medi Ambient (Estudis de la Qualitat Ecològica dels Rius, 6). 171 RESH, V. H. & UNZICKER, J. D. 1975. Water quality monitoring and aquatic organisms: the importance of species identification. J. Water Pollut. Control Fed., 47: 9-19. , V. H. (1992). Recent trends in the use of trichoptera in water quality monitoring. Proc. 7 Int. Symp. Trichoptera, 285-291. ES, S.; TORO, M.; NUÑO, C.; AVILÉS, J.; ALBA-TERCEDOR, J.; ÁLVAREZ, M.; ROBLES, S.; CASAS, J.; JÁIMEZ-CUÉLLAR, P.; MELLADO, A.; MUNNÉ, A.; PA SUÁREZ, M. L. & VIDAL-ABARCA, M. R. (in press). Descripción de las cuencas mediterráneas seleccionadas en el proyecto GUADALMED. Limnética. ROSS, D. H. & WALLACE, J. B. (1982). Factors influencing the longitudinal distribution of larval Hydropsychidae (Trichopt Hydrobiologia, 96: 185-199. , G. P., PICKERING, T. D., & REYNOLDS, N. R. M. (1993). The impact of livestock farming on Welsh streams: The development and testing of a rapid biological method for use in the assessment and control of organic pollution from farms. Envir. Pollut., SIMPSON, K. W. (1980). Abnormalities in the tracheal gills of aquatic insects collected from streams receiving chlorinated or crude oil wastes. Freshwat. Biol., 10: 581-583. SIMPSON, J. C.; PINDER, A. M.; CALE, D. J.; HORWITZ, H. J.; DAVIS, J. A.; YUNG, F. H.; NORRIS, R. H. & HALSE, S. A. (1999). AusRivAS: using macroinvertebrates to assess ecological condition of rivers in Western Australia. Freshwat. Biol., 41: 269-282. STUIJFZAND, S. C.; ENGELS, S.; VAN AMMELROOY, E. & JONKER, M. (1999). Caddisflies (Trichoptera: Hydropsychidae) used for evaluating water quality of large Europe Arch. Environm. Contam. Toxicol., 36: 186-192. 329
Chapter 8 SUÁR Segura. TER B 1. TORO NUÑO, C.; VIVAS, S.; BONADA, N.; PRAT, N.; ALBA- ARCA, M. R. (in press). Calidad de las USSE environmental changes of the Rhone River at Lyons over the last twenty-five VERD factors in Dutch inland waters. Proc. 7th EZ, M. L. y VIDAL-ABARCA, M. R. (2000). Aplicación del índice de calidad del bosque de ribera, QBR (Munné et al., 1998) a los cauces fluviales de la cuenca del río Tecnología del Agua, 201: 33-45. RAAK, C. J. F. & LOOMAN, C. W. N. (1986). Weigthed averagins, logistic regression and the Gaussian response model. Vegetatio, 65: 3-1 TER BRAAK, C. J. F. & VAN DAM, H. (1989). Inferring pH from diatoms: a comparision of old and new calibration methods. Hydrobiologia, 178: 209-223. , M.; ROBLES, S.; AVILÉS, J.; TERCEDOR, J.; CASAS, J.; GUERRERO, C.; JAIMEZ-CUÉLLAR, P.; MORENO, J. L.; MOYÁ, G.; RAMÓN, G.; SUÁREZ, M. L.; VIDAL-AB aguas de los ríos mediterráneos del proyecto Guadalmed. Características físico-químicas. Limnética. TRABAUD, L. (1981). Man and Fire: Impacts on mediterranean vegetation. In: di Castri, FR.; Goodall, D. W. & Specht, R. W. (eds.). Mediterranean-Type Shrublands. Elsevier, New York. 643pp. GLIO-POLATERA, P. & BOURNAUD, M. (1989). Trichoptera and Ephemeroptera as indicators of years. Regulated Rivers, 4: 249-262. ONSCHOT, P. F. M. & HIGLER, L. W. G. (1992). Optima and tolerances of Trichoptera larvae for key Int. Symp. Trichoptera: 293-296. VIEIRA-LANERO, R.(1996). Contribución al conocimiento de las larvas de algunos Tricópteros (Insecta:Trichoptera) de Galicia. MSc. Universidad de Santiago de Compostela.111pp. VIEIR A-LANERO, R. (2000). Las larvas de los tricópteros de Galicia (Insecta:Trichoptera). PhD. Universidade de Santiago de Compostela. 611pp. VUORI, K. M. (1995). Species- and population-specific responses of translocated hydropsychid larvae (Trichoptera, Hydropsychidae) to runoff from acid sulphates soils in the River Kyrönjoki, western Finland. Freshwat. Biol., 33: 305-318. VUORI, K. M. & KUKKONEN, V. K. (2002). Hydropsychid (Trichoptera, Hydropsychidae) gill abnormalities as morphological biomarkers of stream pollution. Freshwat. Biol., 47: 1297- 1306. WALLACE, I. D.; WALLACE, B. & PHILIPSON, G. N. (1990). A key to the case-bearing caddis larvae of Britain and Ireland. Sci. Publs. Freshwat. Biol., 51. 237pp. WARINGER, J. & GRAF, W. (2002). Trichoptera communities as a tool for assessing the ecological integrity of Danubian floodplains in Lower Austria. Proc. 10 tera — Nova Suppl. Ent., 15: 617-623. WIBE f Trichoptera in Danish streams. Freshwat. WIEN ties 1. Foundations and patterns. Cambridge Chapman & Hall. New York. 508-557pp. sects, with species reference to Trichoptera. Ecology, 59: WRIG th Int. Symp. Trichop WESTMAN, W. E. (1991). Measuring realized niche spaces: climatic response of chaparral and coastal sage scrub. Ecology, 72: 1678-1684. WHITTAKER, R. H. (1967). Gradient analysis of vegetation. Biol. Review, 42: 207-264. RG-LARSEN, P.; BRODERSEN, K. P.; BIRKHOLM, S.; GRØN, P. N. & SKRIVER, J. (2000). Species richness and assemblage structure o Biol., 43: 633-647. S, J. A. (1989). The ecology of bird communi University Press. Cambridge. WIEDERHOLM, T. (1984). Responses of aquatic insects to environmental pollution. In: Rosenberg, D. M. & Resh, V. H. (eds.). Freshwater biomonitoring and benthic macroinvertebrates. WIGGINS, G. B. & MACKAY, R. J. (1978). Some relationships between systematics and trophic ecology in Neartic aquatic in 1211-1220. HT, J. F. (1995). Development and use of a system for predicting the macroinvertebrate fauna in flowing waters. Aust. J. Ecol., 20: 181-197. WRIGHT, J. F.; ARMITAGE, P. D. & FURSE, M. T. (1989). Prediction of invertebrate communities using stream measurements. Regulated Rivers, 4: 147-155. 330
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Departament d’Ecologia Facultat d
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Als rius
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Agraïments Ara que miro enrera, me
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Als companys del GUADALMED per have
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Chapter 6 ─ Trichoptera (insecta)
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Resum Hi ha cinc regions en el món
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Resum Factors històrics Factors ec
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Resum METODOLOGIA CAPÍTOL 1: Un pr
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Resum Capítol 1. De manera general
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Resum conca Mediterrània (65% de s
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Resum importants al sud-oest austra
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Resum Els resultats mostraren que l
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Resum No s’han trobat diferèncie
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Resum OBJECTIUS Capítol 6 Presenta
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Resum comunitats de tricòpters tro
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Resum elevades salinitats (probable
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Resum d’asimetria fluctuant i, pe
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Brief introduction and objectives T
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Brief introduction and objectives H
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Brief introduction and objectives 3
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Chapter 1 (Karr, 1981, 1996) using
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Chapter 1 Figure 1. Segura basin an
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Chapter 1 PROTOCOL 2: The samples c
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Chapter 1 Macroinvertebrates: effec
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Chapter 1 % similarity Figure 4. De
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Chapter 1 number of taxa ISASPT 28
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Chapter 1 are some differences in t
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Chapter 1 results got in the field
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Chapter 1 The more appropriate taxo
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Chapter 1 Protocol 1. Non-reference
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Chapter 1 CORKUM, L. D. (1989). Pat
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Chapter 1 RESH , V. H.; NORRIS, R.
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Chapter 1 Annex 1. List of taxa fou
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Chapter 2 The organisms more used t
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Chapter 2 Palmiet basins were selec
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Chapter 2 calcareous and sedimentar
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Chapter 2 Similarities and differen
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Chapter 2 1 0 -1 Spain B24-RLB24-SV
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Chapter 2 200 160 120 80 40 0 40 30
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Chapter 2 macroinvertebrate fauna o
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Chapter 2 methodology yield better
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Chapter 2 VIDAL-ABARCA, M.R.; VIVAS
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Chapter 2 NORRIS, R. H. & GEOREGES,
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Chapter 2 82
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Chapter 3 whereas summers are hot w
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Chapter 3 When first explorers arri
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Chapter 3 stream in the most humit
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Chapter 3 studies at multiple scale
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Chapter 3 ecoregion; 4 in “Northe
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Chapter 3 Project was to establish
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Chapter 3 condition this method is
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Chapter 3 Table 2. Exclusive and ub
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Chapter 3 Chile and SAustralia have
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Chapter 3 Differences between all s
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Chapter 3 the abundants Caenidae, H
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Chapter 3 Mean of % relative abunda
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Chapter 3 For the rest of med-regio
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Chapter 3 The values of IV-values f
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Chapter 3 Temporary sites are chara
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Chapter 3 but not for MedBasin and
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Chapter 3 Table 9. IndVal results b
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Chapter 3 CALIFORNIA 70.8% MEDBASIN
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Chapter 3 Geological connexions Com
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Chapter 3 In spite of these observe
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Chapter 3 multivoltine life cycles
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Chapter 3 intermittency, flood freq
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Chapter 3 Other convergences and di
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Chapter 3 BALL, I. R. (1975). Natur
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Chapter 3 DE MOOR, F. C. (1992). a.
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Chapter 3 GENTILLI, J. (1989). Clim
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Chapter 3 LOGAN, P. & BROOKER, M. P
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Chapter 3 PRAT, N. 1993. El futuro
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Chapter 3 Minshall, G. W. (eds.). S
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Chapter 3 Annex 1. Presence and abs
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Chapter 3 California MedBasin Chile
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Chapter 3 Plate 1. Characteristics
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Chapter 4 Lake, 1992; Cooper et al.
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Chapter 4 Coastal Ranges SAN FRANCI
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Chapter 4 IndVal method (Dufrêne &
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Chapter 4 the bottom have a similar
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Chapter 4 Figure 4. Bray-Curtis clu
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Chapter 4 because methodologies, sa
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Chapter 4 mediterranean areas in th
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Chapter 4 DELUCCHI, C. M. (1989). M
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Chapter 4 168
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Chapter 5 distribution of organisms
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Chapter 5 & Allan, 1995). The level
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Chapter 5 samples were preserved wi
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Chapter 5 Data analysis Seasonal ch
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Chapter 5 Macroinvertebrates and te
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Chapter 5 As a change in the flow c
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Chapter 5 2 1 0 -1 -2 1 0 -1 -2 Ca
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Chapter 5 number of taxa 45 40 35 3
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Chapter 5 Results from the 4 th Cor
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Chapter 5 flow species”. They dis
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Chapter 5 As Townsend and Hildrew (
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Chapter 5 a mix of riffles/pool/cor
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Chapter 5 Although natural disturba
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Chapter 5 GRAY, L. J.; FISHER, S. G
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Chapter 5 RESH, V. H.; JACKSON, J.
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Chapter 5 Annex 1. Physical structu
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Chapter 5 Annex 3. Biological trait
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Chapter 5 Annex 5. Maximum affinity
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Chapter 6 high number of endemic sp
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Chapter 6 Checklist structure and t
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Chapter 6 This species has been rec
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Chapter 6 DISTRIBUTION AND ECOLOGY
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Chapter 6 11- Rhyacophila pascoei M
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Chapter 6 1984), specially to suspe
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Chapter 6 This species can be found
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Chapter 6 Figure 3. Cephalic head f
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Chapter 6 47- Tinodes maclachlani K
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Chapter 6 64- Drusus rectus (McLach
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Chapter 6 pieces of litter arranged
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Chapter 6 Tordera Basin: ToM6, ToM7
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Chapter 6 Although M. aspersus have
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Chapter 6 Superfamily LEPTOCEROIDEA
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Chapter 6 TRIBU Triaenodini Morse,
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Chapter 6 Schizopelex McLachlan, 18
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Chapter 6 present a European distri
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Chapter 6 REFERENCES BALLETTO, E. &
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Chapter 6 PRAT, N.; PUIG, M. A. & G
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Chapter 6 Annex 1. Sampling sites w
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Chapter 6 MIJARES BASIN TURIA BASIN
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Chapter 6 GUADALQUIVIR BASIN Site c
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Chapter 7 (e.g., Ormerod & Edwards,
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Chapter 7 Figure 1. Basins sampled
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Chapter 7 taken until no more famil
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Chapter 7 Geomorphological variable
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Chapter 7 Seasonal changes in caddi
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Chapter 7 Table 2. Maximum abundanc
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Chapter 7 headwaters at high altitu
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Chapter 7 Table 4. Pearson correlat
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Page 297 and 298: Chapter 7 high significant of each
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Page 305 and 306: Chapter 7 AUSTIN, M. P., & GREIG-SM
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Page 311 and 312: Chapter 7 ZAMORA-MUÑOZ, C.; ALBA-T
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Page 315 and 316: Chapter 7 Annex 3. Taxa’s codes C
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Page 327 and 328: Chapter 8 O&T for IBMWP O&T for QBR
Page 329 and 330: Chapter 8 O&T for SS O&T for SULPHA
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Page 337 and 338: Chapter 8 DISCUSSION The wide range
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Page 341: Chapter 8 DOHET, A. (2002). Are cad
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Page 357 and 358: Chapter 9 Similarly to levels of FA
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Page 363 and 364: Chapter 9 MERILÄ, J. & BJORKLUND,
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Page 367 and 368: Conclusions 4. Responses to tempora
Page 369 and 370: Conclusions 356
Page 371 and 372: Conclusions 358
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