Research Article |
Corresponding author: Silvia Poponessi ( silvia.poponessi@hotmail.it ) Academic editor: Marta Puglisi
© 2020 Silvia Poponessi, Michele Aleffi, Marko S. Sabovljević, Roberto Venanzoni.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Poponessi S, Aleffi M, Sabovljević MS, Venanzoni R (2020) Bryophyte diversity hotspot: the Marmore Waterfalls Regional Park (Umbria, central Italy). Italian Botanist 10: 33-45. https://doi.org/10.3897/italianbotanist.10.54885
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A study of the bryophyte of Marmore Waterfall Natural Park a very peculiar territory for its geological, biogeographical and bioclimatic traits, was carried out. The reported data were collected in the valley area of ‘Parco Fluviale del Nera’ Regional Park, where the waters are flowing and the humidity of the rocks is oozing. Research led to the identification of 101 taxa of bryophytes (21 liverworts and 80 mosses), among which two liverwort and 10 moss species are new records for the Umbria region, while four are confirmed. The study offers new outcomes on neglected aspects of the flora of central Italy and represents a considerable improvement of the floristic, biogeographical and ecological understanding of its bryophytic component. Additionally, the area turn out to be significant from the conservation point of view both nationally and internationally considering that it harbours high diversity of bryophytes species among which many rare, threatened and interesting species occur. Eighteen species of conservation interest in Italy are recorded during the latest investigation (all in category NT – near threatened). Additionally two species that are considered data deficient in Italy are present in the researched area (Conocephalum salebrosum and Fissidens curvatus). Also, there is a small populations of a species vulnerable (Marchantia paleacea), endangered (Bryum calophyllum) and data deficient (Fissidens curvatus and Barbula bolleana) in European scale.
Bryophyte, ecology, Habitats Directive 92/43/EEC, liverworts, mosses, Petrifying springs, Umbria
The Regional Park Marmore waterfalls are man-made waterfalls, built by ancient Romans at 271 BC for tried to solve the problem of the Velino River and Valnerina weatlands and, at the same time, to use the water resource both for the agriculture and as a source of power. With a total height of 165 m, it is one of the highest man-made waterfalls in Italy and worldwide.
The Marmore Falls is located in the Umbrian Region (42°33'23"N, 12°42'73"E) near the Terni city at 218 m above sea level, within the Valnerina valley in the ‘Parco Fluviale del Nera’ Regional Park (Fig.
The vegetation type “Cratoneurion commutati” was first described by Walo Koch in his 1928 monograph ‘Die höhere Vegetation der subalpinen Seen und Moorgebiete des Val Piora’. This alliance (sometimes shortening the name to Cratoneurion) as fresh-water, lime-rich spring communities with frequent tufa formation, is found especially in the montane and sub-Alpine zone, in which the ground layer consisted of mosses (
The first bryological explorations made at the Marmore Falls date back to 1869 where author recorded for the first time in the Umbria Region of the tufa moss Cratoneuron commutatum (Hedw.) Roth, currently Palustriella commutata (Hedw.) Ochyra (
The particular environment, with a gorge and waterfall (Fig.
The site of the park, has been examined from a bryological point of view in the year 2008 during a single inspection and in the years 2012–2018 with repeatedly investigation (especially from October to March, even twice a month). Collectors have inspected the area almost always on the same day or alternatively. The transect methodology was applied with aim to cover as much as possible habitat and microhabitat types, with special emphasis on wet habitats. We also investigated in a less hydrophilic context, poor in cormophytic vegetation and with a more mineral substrate. The exsiccata were stored in the Herbarium PERU of the Department of Chemistry, Biology and Biotechnologies, University of Perugia and labels will be available soon on web http://www.anarchive.it (
The research conducted resulted in identification of 101 bryophytes taxa: 21 liverworts and 80 mosses. According to
Liverworts
Aneura pinguis (L.) Dumort.: on the bank of the Velino river.
Apopellia endiviifolia (Dicks.) Nebel & D. Quandt: very abundant in the study area. Grows on wet rock.
* Cephaloziella baumgartneri Schiffn.: on dry rock at the entrance to damp cavities.
Cololejeunea rossettiana (C.Massal.) Schiffn.: abundant on base rich substrate.
Conocephalum conicum (L.) Dumort.: very abundant near the waterfall and in the study area.
Conocephalum salebrosum Szweyk., Buczk. & Odrzyk.: locally abundant at entrance to “Grotta degli Innamorati”.
# Jungermannia atrovirens Dumort.: abundant on damp limestone.
Lejeunea cavifolia (Ehrh.) Lindb.: on rocks and trees in shaded and humid places.
Lophocolea bidentata (L.) Dumort.: abundant in damp places.
Lunularia cruciata (L.) Dumort. ex Lindb.: particularly in damp, shady places.
Marchantia paleacea Bertol.: on damp limestone.
Marchantia polymorpha subsp. polymorpha: very abundant in damp and shady places.
* Marchantia polymorpha subsp. montivagans Bischl. & Boissel.-Dub.: only presence on lightly shaded and base-rich soil.
# Marchantia polymorpha subsp. ruderalis Bischl. & Boissel.-Dub.: on disturbed habitats, at the edges of the tourist trails.
Marchantia quadrata Scop.: grows on dry rock.
Mesoptychia turbinata (Raddi) L.Söderstr. & Váňa : on calcareous substrates.
Pellia epiphylla (L.) Corda: on shaded banks.
Porella platyphylla (L.) Pfeiff.: on bark of Alnus glutinosa (L.) Gaertn.
Radula complanata (L.) Dumort.: on bark of Alnus glutinosa and Fraxinus excelsior L.
# Reboulia hemisphaerica (L.) : on limestone pavement and on earthy.
Solenostoma gracillimum (Sm.) R.M.Schust.: on soft rock.
Southbya tophacea (Spruce) Spruce: on limestone rock.
Mosses
Barbula unguiculata Hedw.: disturbed and open habitats.
Brachytheciastrum velutinum var. velutinum: on stones and compacted soil.
Brachythecium rivulare Schimp.: on runnels and wet ledges.
Brachythecium rutabulum var. rutabulum: very abundant on rock and walls.
Bryum calophyllum R.Br.: on soil along waterways.
*Bryum gemmiparum De Not.: on dry walls.
Calliergonella cuspidata (Hedw.) Loeske: on dry walls, rock and soil.
Cratoneuron filicinum (Hedw.) Spruce: near the cascade.
Ctenidium molluscum (Hedw.) Mitt.: on dry rock.
Didymodon fallax (Hedw.) R.H.Zander: on wet soil and rock.
Didymodon ferrugineus (Schimp. ex Besch.) M.O.Hill: on dry soil.
Didymodon insulanus (De Not.) M.O.Hill: on walls.
*Didymodon spadiceus (Mitt.) Limpr.: on soil and limestone rock.
Didymodon tophaceus (Brid.) Lisa: on limestone rock.
Encalypta streptocarpa Hedw.: on limestone rock.
Eucladium verticillatum (With.) Bruch & Schimp.: on wet limestone rock.
Exsertotheca crispa (Hedw.) S.Olsson, Enroth & D.Quandt: on limestone rock and walls in lightly shaded sites.
Fissidens bryoides var. bryoides: on streamsides.
Fissidens crassipes subsp. warnstorfii (M.Fleisch.) Brugg.-Nann.:
Fissidens crassipes subsp. crassipes: on wet rock.
Fissidens crispus Mont.: on soil.
Fissidens curvatus Hornsch.: on soil.
Fissidens exilis Hedw.: on soil.
Fissidens osmundoides Hedw.: on limestone rock and walls in lightly shaded sites.
Fissidens rufulus Bruch & Schimp.: immersed in the water.
Fissidens serrulatus Brid.: on limestone rock and walls in lightly shaded sites.
Fissidens taxifolius subsp. taxifolius: is common on soil or in cracks and crevices in rock.
#Gymnostomum calcareum Nees & Hornsch.: on limestone rock.
Homalothecium sericeum (Hedw.) Schimp.: on dry places.
Hydrogonium bolleanum (Müll. Hal.) A. Jaeger: on dripping stone wall.
Hygroamblystegium fluviatile (Hedw.) Loeske: on fast-flowing streams.
Hygroamblystegium tenax (Hedw.) Jenn.: on wet substrate.
Hygroamblystegium varium (Hedw.) Mönk. subsp. varium: on wet substrate.
*Hymenostylium recurvirostrum var. recurvirostrum: on soil with high-humidity.
Hypnum cupressiforme var. cupressiforme: on the bark of Ostrya carpinifolia Scop.
Hypnum cupressiforme var. filiforme Brid.: on the bark of Ostrya carpinifolia.
Imbribryum mildeanum (Jur.) J.R.Spence: on wet rock.
Isothecium alopecuroides (Lam. ex Dubois) Isov.: on limestone rock.
Kindbergia praelonga (Hedw.) Ochyra: on wet rock.
Leptodon smithii (Hedw.) F.Weber & D.Mohr: on the bark of Ostrya carpinifolia.
Leucodon sciuroides (Hedw.) Schwägr.: on the bark of Ostrya carpinifolia.
* Mnium hornum Hedw.: on wet rock and soil.
Mnium stellare Hedw.: on wet soil.
Orthotrichum diaphanum Schrad. ex Brid.: on the bark of Ostrya carpinifolia.
Oxyrrhynchium hians (Hedw.) Loeske: on the wet soil and rock.
Oxyrrhynchium speciosum (Brid.) Warnst.: on the wet soil and rock.
Palustriella commutata (Hedw.) Ochyra: present along the vertical walls to waterfall.
*Palustriella falcata (Brid.) Hedenäs: present along the vertical walls to waterfall.
Plagiomnium affine (Blandow ex Funck) T.J.Kop.: on the wet soil.
Plagiomnium cuspidatum (Hedw.) T.J.Kop.: on the wet soil.
*Plagiomnium elatum (Bruch & Schimp.) T.J.Kop.: on the wet soil.
Plagiomnium ellipticum (Brid.) T.J.Kop.: on the wet soil.
Plagiomnium undulatum (Hedw.) T.J.Kop.: on the wet soil.
Plasteurhynchium meridionale (Schimp.) M.Fleisch.: on soil.
Pleurozium schrebei (Willd. ex Brid.) Mitt.: on limestone soil.
*Pohlia annotina (Hedw.) Lindb.: on wet soil.
*Polia melanodon (Brid.) A.J.Shaw: on wet soil.
Pohlia wahlenbergii var. wahlenbergii: on limestone soil near the cascade.
Pseudoscleropodium purum (Hedw.) M.Fleisch.: among rocks and on rock ledges.
Ptychostomum archangelicum (Bruch & Schimp.) J.R.Spence: among rocks and on rock ledges.
Ptychostomum capillare (Hedw.) Holyoak & N.Pedersen: among rocks and on rock ledges.
Ptychostomum donianum (Grev.) Holyoak & N.Pedersen: on soil.
Ptychostomum imbricatulum (Müll.Hal.) Holyoak & N.Pedersen: on soil.
Ptychostomum torquescens (Bruch & Schimp.) Ros & Mazimpaka: on limenstone soil and rock.
Rhizomnium punctatum (Hedw.) T.J.Kop.: on soil.: on damp or wet soil.
Rhynchostegiella tenella var. tenella: on limestone rock.
Rhynchostegium confertum (Dicks.) Schimp.: on rock and walls.
Rhynchostegium megapolitanum (Blandow ex F.Weber & D.Mohr) Schimp.: accumulated soil on walls.
Rhynchostegium riparioides (Hedw.) Cardot: on along the banks of rivers.
Scorpiurium circinatum (Bruch) M.Fleisch. & Loeske: on rocks and the base of trees.
Syntrichia leavipila Brid.: on walls and rocks.
Tortella inflexa (Bruch) Broth.: on limestone rock.
Tortella tortuosa var. tortuosa: on moist, often shaded or sheltered rocks and walls.
*Tortula marginata (Bruch & Schimp.) Spruce: on moist, often shaded or sheltered rocks and walls.
Trichostomum crispulum Bruch: on shaded calcareous.
*Weissia brachycarpa (Nees & Hornsch.) Jur.: On wet soil.
Weissia controversa var. controversa: on damp, bare soil.
*Weissia rutilans (Hedw.) Lindb.: on damp, bare soil.
Zygodon rupestris Schimp. ex Lorentz: on the bark of old trees.
The results of this survey bring undoubtly the idea of significance of this area as one of the region of high bryophytes diversity. Though, the hydrogeology of the investigated area is so peculiar per se, it offers so many microhabitat types that also this aspect should be taken into consideration when estimated this zone natural peculiarities.
The bryophytic flora and its role in the deposition of active travertines has been well documented over time (
The reported bryophytic survey shows a high level of floristic and biogeographical diversity for a Priority Habitat 7220 and gorge of the Marmore waterfall. It significantly improves the knowledge of a territory, which was already known for providing peculiar habitats for rare and endangered bryophytes taxa (
Additionaly, ecologically contrasting species like mesophilic Rhynchostegiella tenella, and more xerophilic (Ctenidium molluscum, Leucodon sciuroides) are often recorded in short distance one from another suggesting transitional gradient of habitat condition in very small scale. Some species are rather plastic from the point of view of their water requirements and habitat water regime (Barbula unguiculata, Brachythecium rutabulum), and can be recorded in range of microhabitat type suggesting wider ecological valences, and genetic plasticity.
In the sence of biomass and abudance Palustriella commutata (syn. Cratoneuron commutatum (Hedw.) G. Roth), is the species characteristic to Priority Habitat 7220, and it is well presented along the vertical walls to Marmore waterfall. It forms almost monospecific pillows which constitute the portion of active deposition to travertines. In other portions of the waterfall, where the formation of travertine remains active, generally we observed the repetitive composition of the following species: Brachythecium rivulare, Barbula bolleana, Bryum gemmiparum, Conocephalum conicum, Cratoneuron filicinum, Didymodon tophaceus, Eucladium verticillatum, Hymenostylium recurvirostrum, Jungermannia atrovirens, Palustriella commutata, Pellia endiviifolia, Rhynchostegium riparioides which is in accordance with the similar sites reported elsewhere (e.g.
The taxa that repeatedly and most frequently occurred in the limestone portion with dripping and/or oozing rock were: Eucladium verticillatum, Conocephalum conicum, Pellia endiviifolia, Barbula bolleana, Gymnostomum calcareum and Didymodon tophaceus
Eucladium verticillatum, tended to grow on steeper, more sheltered terrain. This acrocarp moss was absent from sites with high water flow and it gained moisture mainly from spray or capillarity. Unlike P. commutata which forms almost monospecific pillows and is definitely the moss significant in tufa formation as considered its biomass, E. verticillatum was often intermixed with other species also not of great biomass. Among others Didymodon tophaceus and Gymnostomum calcareum were mostly recorded as associate species.
Three species among bryophytes recorded were categorized as Potentially Negative Indicator Species, depend on the circumstances in which they occurred. Cratoneuron filicinum, Brachythecium rivulare and Platyhypnidium riparioides can be indicative of nutrient enrichment, especially elevated phosphate levels. However, these species (especially C. filicinum) can occur individually at low levels of abundance in springs with Good water quality, where they form part of a mixed bryophytes assemblages along with other characteristic petrifying spring species (
Cephaloziella baumgartneri and Marchantia polymorpha subsp. montivagans are newly recorded liverworts taxa for the Umbria Region. Additionally, M. polymorpha subsp. montivagans is rare in central and southern Italy. They are localized along the Nera river where the banks flow into the tourist route of the Marmore Didactic Centre. M. polymorpha subsp. ruderalis is confirmed for the flora of Region and it is localized along antropogenic pathway. The most abundant liverworts in the investigated area were C. conicum and P. endiviifolia. They occur in moist, shaded positions and seems to be strongly restricted to calcareous substrates. Indeed they grow frequently along streams, bases of moist rocks and cliffs, and especially near the waterfalls.
All liverworts recorded at the Marmore waterfall are very interesting from biodiversity point of view of this park. The region is also very significant in harbouring such a lot liverwort species that are Near Threatened (NT) nationally. According to IUCN criteria they are likely to qualify for a threatened category in the near future. Conocephalum salebrosum is evalutated Data Deficient (DD) in Italy, since it was recently reported for Umrbia and Italy in the Marmore waterfall area (
Marchantia paleacea is a rare liverwort in central and southern Italy (
Weissia rutilans is a rare moss in Italy (
Other taxa recorded for the first time in the Umbria Region are: Didymodon spadiceus, Hymenostylium recurvirostrum var. recurvirostrum, Mnium hornum, Palustriella falcata, Plagiomnium elatum, Pohliaannotina, P. melanodon, Tortula marginata and Weissia brachycarpa. These are all significant bryophytes representatives of high-humidity stands, habitat types that in time of severe climate changes undergo strong decrease especially in southern Europe.
Barbula bolleana is very rare in Italy but very abundant in this habitat in the investigated area, which consists of a dripping stone wall, with chalky incrustations at its base, suggesting it takes an active part in the formation of tufa. B. bolleana is a hygrophilous and calcareous moss for the first time reported on the Marmore Falls site according to
An interesting acrocarp moss found in Marmore Waterfall is Fissidens rufulus and it has been firstly reported for Umbria Region recently (
Ecologically significant species of petrifying springs which serve as positive indicators of habitat status consist largely of mosses and liverworts, with a smaller number of vascular plants. Rather high diversity of bryophytes is not proportional to small surface of studied areas. This is a consequence of the high portion of microhabitat types and quick gradient changes from ecological humid situations to shaded humid and irradiated dry sites. Also, from the bryological point of view protected area of Parco Fluviale del Nera’ Regional Park is a habitat of many regionally, nationally threatened and scarce species and harbour a good population of species of European conservation interest. Further studies and monitoring programs are welcomed in future with aim to maintain survival of national and European significant bryophytes species. During these years of study, Carmela Cortini Pedrotti Bryological Path was established. Entitled to Professor Cortini, who spent her life studying bryophytes (1931–2007). She is forever remembered for her work with, and great knowledge of Bryophyte. The path runs along the tourist trail number 2 of the waterfall site and has been enriched with information boards concerning the bryophytes that have been found in the site and along the path.