ACTA BIOLOGICA SLOVENICA LJUBLJANA 2010 Vol. 53, Št. 2: 33-43 ЛВ Environmental assessment and macrophytes of the watercourses Bloščica and Cerkniščica Okoljska ocena in makrofiti vodotokov Bloščice in Cerkniščice Špela Mechora1, Urška Kuhar1, Mateja Germ1* 1Biotechnical Faculty, Department of Biology, Večna pot 111, 1000 Ljubljana, Slovenia Correspondence: mateja.germ@bf.uni-lj.si Abstract: The aim of the present work was to determine the abundance and distribution of macrophytes in streams Bloščica and Cerkniščica and to establish the relation between environment characteristics and abundance of macrophytes. The environmental and macrophytes' inventory was made on the whole length of the watercourse. We determined a presence, abundance and growth form of macrophytes and environmental parameters according to modified RCE Inventory. Nineteen taxa were found in the watercourse Bloščica and 20 taxa in the watercourse Cerkniščica. Canonical correspondence analysis revealed that six environmental parameters significantly affected macrophyte community, the most influential being bottom structure, the width of riparian zone, retention devices in a channel and the land use beyond the riparian zone. Key words: environmental assessment, macrophytes, watercourses Izvleček: V prispevku podajamo rezultate raziskav pojavljanja, razporeditve in pogostosti mak-rofitov v vodotokih Bloščica in Cerkniščica ter ugotavljamo povezavo med okoljskimi razmerami in pojavljanjem makrofitov. Makrofite, njihovo pogostost, rastno obliko in stanje širšega vodnega okolja po prirejeni RCE metodi, smo popisali na celotni dolžini izbranih vodotokov. V vodotoku Bloščica smo popisali 19 taksonov, v vodotoku Cerkniščica pa 20 taksonov. Kanonična korespondenčna analiza je pokazala, da šest okoljskih parametrov značilno vpliva na pojavljanje in pogostost makrofitov. Največji vpliv imajo struktura dna, širina obrežnega pasu, zadrževalne strukture v strugi in zaledje. Ključne besede: okoljska ocena, makrofiti, vodotoki Introduction Rivers are diverse and dynamic systems that play an important role in the complexity of the landscape (Chovanec et al. 2000). Macrophytes are fundamental to the structure and functioning of lowland river habitats (Baatrup-Pedersen and Riis 1999). Distribution and abundance of macrophytes are affected by several environmental and antropogenic factors and their interactions (Lacoul and Freedman 2006). Parameters exerting impact on macrophyte's growth and abundance in running waters are the following: climate, hydrology, geomorphology, nutrients and other chemi- cal factors, biological interactions and human activities (Onaindia et al. 1996, Bernez et al. 2004, Hrivnàk et al. 2007). Ecological status of rivers is influenced by human activities that affect the physical properties of the riverbed, riparian vegetation and land beyond the riparian zone (Petersen 1992). These changes worsened the conditions of the river ecosystem and water quality as well as altered communities of aquatic organisms, including macrophytes, which play important roles in energy flow, nutrient cycling and sedimentation processes (Holmes 1999, Gaberščik et al. 2003). Macrophytes improve water quality, both directly through oxygenation and nutrient recycling, and indirectly by providing surface for water-purifying algae, fungi and bacteria (Holmes 1999). Species composition of macrophytes and their abundance reflect the quality of an ecosystem as a whole. For that reason macrophytes are included in the EU Water Framework Directive (Council of the European Communities 2000), presenting one of the four indispensable biological elements, which determine the ecological status of rivers (Dodkins et al. 2005). The aims of the present study were to determine the presence, abundance and distribution of macrophytes in watercourses Bloščica and Cerkniščica and to find out the relation between the environmental parameters and the occurrence of macrophytes. Materials and Methods Study area Watercourses Bloščica and Cerkniščica are located in Notranjska region (Slovenia) in karst area. Almost half of the catchment of both watercourses is covered by forest. The watercourse Bloščica is intermittent watercourse flowing on Bloke plateau being a part of the watershed of the river Ljubljanica. Elevation of its flow ranged from 720 and 750 m. Catchment comprises of small tributaries (Runarščica, Blatni potok, Krajič, Ribjek) covering about 25 km2. Due to its low slope, the watercourse Bloščica flows slowly and makes many meanders. It flows on dolomites first 6 km of its length. At Velike Bloke it cut its bed into limestone and dolomite and finnaly sinks underground. The upper part of the watercourse Bloščica flows mainly through preserved landscape, while the lower part from Ulake downstreams is more affected by human activity. Spring of the about 17 km long watercourse Cerkniščica is located in a hilly area of Sveti Vid and Cajnarji. The catchment comprises 50 km2. It is the biggest surface tributary of the lake Cerknica. The water level changes very quickly in the case of strong rain, so it can be designated as a torrent watercourse. The watercourse Cerkniščica Table 1: List of taxa, determined in the watercourse Bloščica. Tabela 1: Seznam vrst, prisotnih v Bloščici. Taxa Abbreviation Growth form Alisma plantago-aquatìca L. Ali pla am Bryophyta Bryophy sa Chara sp. Cha sp. sp Equisetum palustre L. Equ pal he Lythrum salicaria L. Lyt sal he Mentha aquatica L. Men aqu am Mentha longifolia (L.) Hudson Men lon am Menyanthes trifoliata L. Men tri he Myosotis scorpioides L. Myo sco am Myriophyllum spicatum L. Myr spi sa Nasturtium officinale R. Br. In Aiton Nas off he Petasites hybridus (L.) Gaertner Pet hyb he Phragmithes australis (Cav.) Trin ex Steud. Phr aus he Plantago altissima L. Pla alt he Potamogeton lucens L. Pot luc sa Potamogeton nodosus Poir. Pot nod fl Schoenoplectus lacustris (L.) Palla Sch lac he Sparganium erectum L. Spa ere he, sa Typha latifolia L. Typ lat he Legend: ap = plants floating on the water surface, sp = submerged pleustophytes, sa = submerged anchored plants, fl = floating leaf rooted plants, am = amphiphytes, he = helophytes flows in its upper part in narrow and deep valley. From Cajnarji to Begunje by Cerknica, its bottom becomes wider and steeper, covered by fluvial deposits. At Begunje by Cerknica it flows on karst area. The watercourse Cerkniščica is regulated in the settlements Cerknica and Dolenja vas. It sinks underground at Cerkniško polje. The catchments of both studied watercourses are part of the Natura 2000 network. Riparian, Channel, and Environment Inventory (RCE) Studied watercourses were divided to stretches from 360 to 1030 m long. The start of the new stretch was determined where presence or abundance of macrophytes changed, when we observed changes in land use type, channel characteristics or riparian zone. Every stretch was assessed according to the modified RCE Inventory (Petersen 1992, Germ et al. 2003). RCE Inventory was developed for the assessment of physical condition of the riparian zone and the stream channel in lowland streams, flowing through agricultural landscape. Modified RCE Inventory consisted from 12 parameters, each describing 4 levels of environmental gradient. The parameters include land-use type beyond the riparian zone, characteristics of the riparian zone (width, completeness and vegetation type), and morphology of the stream channel (channel structure, bank structure and undercutting, occurrence of retention structures and sediment accumulation, type of stream bottom and detritus and dynamics of the flow). Figure 1: Distribution of macrophytes in the watercourse Bloščica. Stretch 10 was not surveyed. Slika 1: Razporeditev in pogostost makrofitov v Bloščici. Odsek 10 ni bil pregledan. RPM [%] 5 10 15 d Phr aus Men aqu Men tri Lyt sal Myr spi Spa ere Cha s p. Myo sco Sch lac Pot nod Typ lat Pet hyb Pla alt Men lon Equ pal Pot luc Bryophy Ali pla Nas off Figure 2: Relative plant mass (RPM) of macrophytes in the watercourse Bloščica. Slika 2: Relativna rastlinska masa (RPM) makrofitov v Bloščici. Macrophyte survey The distribution and abundance of macrophytes in studied watercourses were assessed from the source to the outflow, using a boat and a rake with hooks. The abundance was evaluated using a five degree scale as follows (Kohler and Janauer 1995): 1 = very rare; 2 = infrequent; 3 = common; 4 = frequent; 5 = abundant, predominant. Plants were identified using the keys by Preston (1995), Casper and Krausch (1980) and Martinčič et al. (1999). Statistical analysis On the basis of plant abundance, a relative plant mass was calculated (RPM) that is related to true biomass with function x3 (Pall and Janauer 1995, Kohler and Janauer 1995). Canoni- Ali pla Bryophy Cha sp. Equ pal Lyt sal Men aqu Men lon Men tri Myo sco Myr spi Nas off Pet hyb Phr aus Pla alt Pot luc Pot nod Sch lac Spa ere Typ lat Figure 3: The ratio of the length of the watercourse Bloščica overgrown by certain species of macrophytes »d« value; 0.5 for example means that 50 % of watercourse in owergrown with macrophytes. Slika 3: Delež dolžine vodotoka, poraslega z določeno vrsto makrofitov »d« vrednost; 0,5 npr. pomeni, da je 50 % vototoka porastlega z določeno vrsto. cal correspondence analysis (CCA) (Canoco for Windows Version 4.5) was used to assess the relationship between the composition and abundance of macrophytes, and environmental parameters. Environmental parameters were coded numerically from 1 (the most modified or degraded condition) to 4 (the natural or near natural condition). Results Presence and abundance of macrophytes In the watercourse Bloščica 19 taxa of macrophytes was detected on the 17.800 m length (Tab. 1 and Fig. 1). Three species found are listed on the Slovenian Red list of Pteridophyta and Spermatophyta (Ur. l. RS 82/2002) as vulnera- 0 20 25 Figure 4: Distribution of macrophytes in the watercourse Cerkniščica. Slika 4: Razporeditev in pogostost makrofitov v Cerkniščici. ble (Menyanthes trifoliata, Potamogeton lucens and P. nodosus). The highest number of species was found in the stretches 18 (12) and 19 (12). The highest RPM reached Phragmites aus-tralis (20.9 %), followed by Mentha aquatica (17.6 %), Menyanthes trifoliata (12.4 %) and Lythrum salicaria (12.2 %) (Fig. 2). Lythrum salicaria and Mentha aquatica occured in more than 80 % of the watercourse, followed by Me-nyanthes trifoliata (d = 0.77) and Phragmithes australis (d = 0.73) (Fig. 3). The majority of species in the both watercourses had amphibious or helophitic growth form, while submerged species were relatively scarce. In the watercourse Cerkniščica 20 taxa of macrophytes were found (Tab. 2 and Fig. 4). Three of them are listed on the Slovenian Red list of Pteridophyta and Spermatophyta (Ur. l. RS 82/2002) determined as vulnerable: Nym-phaea alba, Potamogeton nodosus and Polygo-num amphibium. The highest RPM reached Petasites hybri-dus (17.5 %), followed by Cirsium oleraceum (13.5 %) and Equisetum palustre (12.4 %) (Fig. 5). Petasites hybridus occured in 85 % of the watercourse, followed by Lythrum salicaria (d = 0.67), Equisetum palustre and Cirsium olera-ceum (d = 0.62) (Fig. 6). Table 2: List of taxa, determined in the watercourse Cerkniščica. Tabela 2: Seznam vrst, prisotnih v Cerkniščici. Taxa Abbreviation Growth form Bryophyta Bryophy sa Caltha palustris L. Cal pal he Chara sp. Cha sp. sp Cirsium oleraceum (L.) Scop Cir ole he Equisetum palustre L. Equ pal he Lythrum salicaria L. Lyt sal he Mentha aquatica L. Men aqu am Mentha longifolia (L.) Hudson Men lon am Myosotis scorpioides L. Myo sco am Myriophyllum spicatum L. Myr spi sa Nymphaea alba L. Nym alb ap Petasites hybridus (L.) Gaertner Pet hyb he Phragmithes australis (Cav.) Trin ex Steud. Phr aus he Polygonum amphibium L. Pol amp am Potamogeton nodosus Poir. Pot nod fl Ranunculus sp. Ran sp. sa Schoenoplectus lacustris (L.) Palla Sch lac he Sparganium erectum L. Spa ere he, sa Typha latifolia L. Typ lat he Veronica anagallis-aquatica L. Ver ana sa Legend: ap = plants floating on the water surface, sp = submerged pleustophytes, sa = submerged anchored plants, fl = floating leaf rooted plants, am = amphiphytes, he = helophytes Environmental parameters and distribution of macrophytes Canonical correspondence analysis (CCA) (Canoco for Windows Version 4.5) was used to assess the relationship between environmental parameters and the composition and abundance of macrophytes in the watercourses Bloščica and Cerkniščica. Six examined parameters significantly affected the variability within the macrophyte community, the most influential were stream bottom type, width and completeness of the riparian zone, occurrence of retention devices, land use beyond the riparian zone and bank undercutting (Fig. 7). The stretches are arranged in the ordination diagram according to the characteristics of environmental parameters in individual stretch. The quality of environmental parameters increases in the direction of the arrows. The stretches of Bloščica and streaches of Cerkniščica were present at different parts of the ordination diagram. Rocky bottom was colonised by taxa Cir-sium oleraceum, Equisetum palustre and Pet-asites hibridus, while the mixture of slime and sand was overgrown by Menyanthes trifoliata, Mentha aquatica and Phragmites australis. The taxon Ranunculus sp. and the species V. anaga-lis-aquatica occurred in stretches surrounded by wetland and forests, while the species S. lacus-tris, P. lucens, Alisma plantago-aquatica and P nodosus preferred open locations. Discussion The Riparian, Channel and Environmental (RCE) Inventory has been developed to assess the physical and biological conditions of small, lowland streams in agricultural areas (Petersen 1992). The modified RCE inventory consists of twelve characteristics, which define the structure of the riparian zone, stream channel mor- RPM [%] 0 5 10 15 20 Pet hyb Gir ole Equ pal Bryophy Men lon Spa ere Phr aus Lyt sal Gha sp. Gal pal Men aqu Myr spi Typ lat Nym alb Pot nod Pol amp Myo sco Ver ana Sch lac Ran sp. Figure 5: Relative plant mass (RPM) of macrophytes in the watercourse Cerkniščica. Slika 5: Relativna rastlinska masa (RPM) makrofitov v Cerkniščici. phology and the biological condition in both habitats. Numerous agricultural point discharges from field present a serious problem threat-ing a good ecological status of watercourses. Wide and complete riparian vegetation has key role in prevention of erosion and retention of organic and even toxic substances (Johnston et al. 1990). Prevailed land use type of the watercourse Cerkniščica in upper part was forest and wet grassland and in lower parts agricultural and urban areas prevailed. Mosses were frequent, because of shading of the channel due to riparian vegetation and water level fluctuations. The river-bed of the watercourse Cerkniščica was channelized in the settlements Cerknica and Dolenja vas and therefore riparian vegetation was scarce or absent. The bottom of the watercourse Bloščica consisted from fine, anaerobic sediment. Pre- Bryophy Cal pal Cha sp. Cir ole Equ pal Lyt sal Men aqu Men lon Myo sco Myr spi Nym alb Pethyb Phr aus Pol amp Pot nod Ran sp. Sch lac Spa ere Typ lat Ver ana Figure 6: The ratio of the length of the watercourse Cerkniščica overgrown by certain species of macrophytes »d« value; 0.5 for example means that 50 % of watercourse in owergrown with macrophytes. Slika 6: Delež dolžine vodotoka, poraslega z določeno vrsto makrofitov »d« vrednost; 0,5 npr. pomeni, da je 50 % vototoka porastlega z določeno vrsto. vailing land use was wood and wet grassland. Riparian vegetation was removed at certain sites, that increased the vulnerability of the watercourse. This is also confirmed with canonical correspondence analysis that revealed that most influential environmental parameters shaping macrophyte community were bottom structure, width of riparian zone, retention devices in the channel and land use beyond the riparian zone. Macrophyte species diversity was relatively low in either of the studied watercourses. 19 taxa were detected in the watercourse Bloščica and 20 in the watercourse Cerkniščica. 14 taxa were present in both watercourses. Important parameter, affecting the growth of macrophytes is light (Hut- d 0,5 Figure 7: CCA ordination diagram showing the relationship between the macrophytes and environmental parameters. Lnd use - land use pattern beyond the riparian zone; R width - width of riparian zone; R compl - completeness of riparian zone; Ret str - retention structures; B undc - bank undercutting; Bottom - stream bottom; • - Bloščica; ■ - Cerkniščica. Codes for macrophyte taxa are given in Table 1 and Table 2. Slika 7: CCA ordinacijski diagram s taksoni makrofitov in spremenljivkami okolja. Lnd use - raba tal v zaledju struge; R width - širina obrežnega pasu; R compl - sklenjenost vegetacije v obrežnem pasu; Ret str -zadrževalne strukture v strugi; B undc - spodjedanje brega; Bottom - dno; • - Bloščica; ■ - Cerkniščica. Oznake za taksone makrofitov so v Tabeli 1 in Tabeli 2. Nas off Pot luc : Ali pla > Pot nod Sch lac Pla alt« x Pol amp X Myr spix »Mya sco RET STR BOTTOM ,.1ip vuJ^^"«Nym alb iBryophy X " Cir ole . LND USE R WIDTH -1.0 1.0 cinson 1975). Shaded parts of the watercourses were scarcely colonised with vascular macro-phytes. Mosses were dominant group of macro-phytes in that stretches. Diversity and distribution of macrophytes in lowland rivers depend on the concentration of nutrients, current velocity and anthropogenic impact (Hrivnàk et al. 2007). Human impact on water ecosystem was less evident in the case of the watercourse Bloščica, where wet grasslands colonising the areas along the watercourse were less appropriate for agricultural use. Similarly, human impact was not prominent in the upper parts of watercourse Cerkniščica, since the area was covered by forests and wet meadows. Six species, listed on the Slovenian Red list (Ur. l. RS 82/2002) as vulnerable, thrive in the sites, where watercourses flow in the natural or little altered landscape with relatively wide riparian zone, and mixed silty and sandy sediment with organic matter as also reveals from previous researches (Kuhar et al. 2009). The decrease of heterogeneity of habitats induces lower diversity of macrophytes (O'Hare et al. 2006). In the watercourse Bloščica fine mate- rial and detritus was the prevailing sediment type, banks predominantly consisted from fine inorganic material. Lower number of macrophytes thereafter reflected the homogeneity of the habitat. Relatively homogeneous habitat was found also in the watercourse Cerkniščica. Flow velocity influences the occurrence of macrophytes (Janauer et al. 2010). Upper part of the watercourse Bloščica had higher slope and fast current velocity. Watercourse became wider downstream, current velocity was slower. In that part of the Bloščica, the variety of macrophytes species was higher. Riis et al. (2000) stated that water chemistry and different tolerance of species to nutrient load determine the distribution of macrophytes. Thus, on the basis on the presence of the certain species of macrophytes, the loading of watercourses with nutrients can be assessed. Acceleration of eutrophication is a consequence of human activity, especially urbanization, agriculture and industry (Germ et al. 2008). Potamogeton lucens grows in eutrophic, relatively deep and on calcareous bedrock flowing lowland streams (Preston 1995) as holds true for the last part of the watercourse Bloščica. Genus Chara was found in both watercourses only in stretches located far from agricultural areas. Species richness of the genus Chara drops when amount of nutrient arises. Bornette and Arens (2002) stated that species in genus Chara are pioneer species in habitats, where disturbance appears very often. In the case of both watercourses water-level fluctuations presented the main disturbance. Myriophil-lum spicatum avoids fast flowing and oligotro-phic waters (Germ and Gaberščik 1999); it was found in the lower parts of studied watercourses. Conclusions 1. In the watercourse Bloščica 19 taxa of macrophytes were detected. Three species found are listed on the Slovenian Red list of Pteridophyta and Spermatophyta as vulnerable namely Menyanthes trifoliata, Potamogeton lucens and P. nodosus. 2. In the watercourse Cerkniščica 20 taxa of macrophytes were found. Three of them are listed on the Slovenian Red list of Pteridophyta and Spermatophyta as vulnerable namely Nymphaea alba, Potamogeton nodosus and Polygonum amphibium. 3. The majority ofspecies in the both watercourses had amphibious and helophytic growth form, while submerged species were relatively scarce. 4. Presence and abundance of macrophytes changed along the watercourses mainly due to land use type, width of the riparian zone and bottom properties. Abundance of macro-phytes in both watercourses was the highest in unshaded stretches with the middle current velocity. Povzetek Namen raziskave je bil ugotoviti pojavljanje, razporeditev in pogostost makrofitov v Bloščici in Cerkniščici. Opisali smo stanje širšega vodnega okolja obeh vodotokov ter povezavo med okoljs-kimi razmerami in pojavljanjem makrofitov. Vodotoka smo razdelili na odseke (24 odsekov na Bloščici, 23 odsekov na Cerkniščici), v katerih smo popisali makrofite. Hkrati s popisom mak-rofitov smo ocenili širše okolje s po Petersenu prirejeno RCE metodo (Germ et al. 2003) in habi-tatne parametre. V obeh vodotokih smo skupno popisali 25 taksonov makrofitov. Večjo pestrost makrofitov smo zasledili na mestih, kjer je vodni tok počasnejši in kjer je vpliv človeka zmanjšan (npr. urbanizirana območja, kmetijske površine). Vodotoka se razlikujeta v habitatnih parametrih in prisotnosti makrofitov. Pomemben je tip sedimenta, saj se rastline lažje ukoreninjajo v bolj trdnem substratu kot v rahlih, finih delcih. V Bloščici se je večinoma pojavljal detrit, v Cerkniščici pa so se ob detritu pojavljali še pesek in skale. Kanonična korespondenčna analiza je pokazala, da šest okoljskih parametrov značilno vpliva na pojavljanje in pogostost makrofitov. Največji vpliv imajo struktura dna, širina obrežnega pasu, zadrževalne strukture v strugi in zaledje. Acknowledgements Support was given by Slovenian Research Agency (ARRS), through the program the Plant Biology (P 1-0212). The financial support is gratefully acknowledged. Literature Baatrup-Pedersen, A., Riis, T., 1999. Macrophyte diversity and composition in relation to substratum characetristics in regulated and unregulated Danish streams. Freshwater Biology, 42, 375-385. Bernez, I., Daniel, H., Haury, J., Ferreira, M.T., 2004. Combined effects of environmental factors and regulation on macrophyte vegetation along three rivers in Western France. River Research and Applications, 20, 43-59. Bornette, G., Arens, M.F., 2002. Charophyte communities in cut-off river channels. The role of connectivity. Aquatic Botany, 73, 149-162. Casper S.J., Krausch H.D. 1980: Süwaßerflora von Mitteleuropa. Pteridophyta und Antophyta. - 1. Teil. Lycopodiaceae bis Orchidaceae. VEB Gustav Fischer Verlag, Jena, 403 pp. Chovanec, A., Schiemer, F., Cabela, A., Gressler, S., Grötzer, C., Pascher, K., Raab, R., Teufl, H., Wimmer, R., 2000. Constructed inshore zones as river corridors through urban areas—the Danube in Vienna. Preliminary results. Regulated Rivers. Research and Management, 16, 175-187. Council of the European Communities, 2000. Directive 2000/60/EC of the European Parliament and of the Council establishing a framework for the Community action in the field of water policy. Official Journal of the European Communities L327, 1-73. Corine Land Cover, 2000. Mapping a decade of change. European Environment Agency, Copenhagen. Dodkins, I., Rippey, B., Hale, P., 2005. An application of canonical correspondence analysis for developing ecological quality assessment metrics for river macrophytes. Freshwater Biology, 50, 891-904. Gaberščik, A., Urbanc-Berčič, O., Kržič, N., Kosi, G., Brancelj, A., 2003. The intermittent Lake Cerknica. Various faces of the same ecosystem. Lakes et Reservoirs. Research and Management, 8, 159-168. Germ, M., Gaberščik, A., 1999. The distribution and abundance od macrophytes of the lowland Ižica River (Slovenia). Acta Biologica Slovenica, 42 (4), 3-11. Germ, M., Gaberščik, A., Dolinšek, M., 2003. Macrophytes of River Ižica - comparison of species composition and abundance in the years 1996-2000. Archiv für Hydrobiologie Supplement, 147/1-2, 181-193. Germ, M., Urbanc-Berčič, O., Janauer, G.A., Filzmoser, P., Exler, N., Gaberščik, A., 2008. Macrophyte distribution pattern in the Krka River - the role of habitat quality. Large Rivers, 18 (1-2), 145-155. Holmes, N.T.H., 1999. British river macrophytes perceptions and uses in the 20th century. Aquatic Conservation. Marine and Freshwater Ecosystems, 9, 535-539. Hrivnàk, R., Ot'ahel'ovà, H., Valachovič, M., 2007. The relationship between macrophyte vegetation and habitat factors along a middle-size European river. Polish Journal of Ecology, 55 (4), 717-729. Hutchinson G.E. 1975: A treatise on Limnology. Volume III. Limnological Botany, John Wiley et Sons, New York, 660 pp. Janauer, A., Schmidt-Mumm, U., Schmidt, B., 2010. Aquatic macrophytes and water current velocity in the Danube River. Ecological Engineering, 36, 1138-1145. Johnston, C.A., Detenbeck, N.E., Niemi, G.J., 1990. The cumulative effect of wetlands on stream water quality and quantity. A landscape approach. Biochemistry, 10, 105-141. Kohler, A., Janauer, G.A., 1995. Zur Methodik der Untersuchungen von aquatischen Makrophyten in Flissgewässern. In: Landsberg H. and Klapper H. (eds.). Handbuch Angewandte Limnologie, Ecomed Verl., Landsberg/Lech., pp 1-22. Kuhar, U., Kržič, N., Germ, M., Gaberščik, A., 2009. Habitat characteristics of threatened macrophyte species in the watercourses of Slovenia. Verhandlungen des Internationalen Verein Limnologie, 30 (5), 754-756. Lacoul, P., Freedman, B., 2006. Environmental influences on aquatic plants in freshwater ecosystems. Environmental Reviews, 14, 89-136. Martinčič A., Wraber T., Jogan N., Ravnik V., Podobnik A., Turk B., Vreš B. 1999: Mala flora Slovenije. Tehniška založba Slovenije, 845 pp. Pall, K., Janauer, G.A., 1995. Die Makrophytenvegetation von Flußstauen am Beispiel der Donau zwischen Fluß-km 2552,0 und 2511,8 in der Bundesrepublik Deutschland. Archiv für Hydrobiologie Supplementband 101, (Large Rivers 9), 91-109. O'Hare, M.T., Baattrup-Pedersen, A., Nijboer, R., Szoszkiewicz, K., Ferreira, T., 2006. Macrophyte communities of European streams with altered physical habitat. Hydrobiologia, 566, 197-210. Onaindia, M., de Bikuna, B.G., Benito, I., 1996. Aquatic plants in relation to environmental factors in Northern Spain. Journal of Environmental Management, 47, 123-137. Petersen, R.C., 1992. The RCE. a Riparian, channel, and environmental inventory for small streams in the agricultural landscape. Freshwater Biology, 27, 295-306. Preston C.D. 1995: Pondweeds of Great Britain and Ireland Botanical Society of the British Isles. London, 352 pp. Riis, T., Sand-Jensen, K., Vestergaard, O., 2000. Plant communities in lowland Danish streams. Species composition and environmental factors. Aquatic Botany, 66, 255-272. Uradni list, 2002. Pravilnik o uvrstitivi ogroženih rastlinskih in živalskih vrst v rdeči seznam. Uradni list RS, 82 - 24.9.2002.