macrophytes as biological element for the assessment and
Transcript
macrophytes as biological element for the assessment and
Biol. Mar. Mediterr. (2010), 17 (1): 67-70 A. Sfriso, C. Facca Department of Environmental Sciences, University of Venice, Calle Larga, S. Marta, 2137, Venice, Italy. [email protected] MACROPHYTES AS BIOLOGICAL ELEMENT FOR THE ASSESSMENT AND MANAGEMENT OF TRANSITIONAL WATER SYSTEMS IN THE MEDITERRANEAN ECOREGION L’ELEMENTO BIOLOGICO MACROFITE PER LA VALUTAZIONE E LA GESTIONE DEGLI AMBIENTI DI TRANSIZIONE NELL’ECOREGIONE MEDITERRANEA Abstract – Macrophytes (macroalgae and angiosperms) are one of the biological quality elements (BQE) proposed by the European Water Framework Directive (WFD, 2000/60/EC) to assess the ecological status of coastal waters and transitional systems. Here the application of the available indices (MaQI, Italy and EEI, Greece) set up to attempt to the WFD requirements for the Mediterranean Ecoregion are presented and applied to 5 Venice Lagoon areas of different ecological status. Indices are based on a different rationale but whereas MaQI can be used also in the presence of a single taxon with a negligible biomass coverage, EEI requires a coverage >30%. Key-words: phytobenthos, aquatic plants, environmental monitoring, MaQI, EEI, Venice Lagoon. Introduction – The first studies that related macrophytes to some environment pollution events go back to the 1970s. Phytosociological studies and the Rhodophyceae/Phaeophyceae ratio (R/P) were the most interesting application of macrophyte vegetation in the coastal waters of Trieste, Marsiglia and in some Sardinia and Sicilia areas but only in the 2000s, under the WFD promotion, the first well structured phytobenthic indices were proposed (Giaccone & Catra, 2004). In 2001, some Greek researchers proposed the application of the Ecological Evaluation Index (EEI) based on the per cent coverage and macrophyte distinction in two functional groups: the late successional (ESG I) and the opportunistic (ESG II) species (Orfanidis et al., 2001, 2003). The index is applied both to coastal and transitional waters and now it is also accepted by Cipro, Slovenia and Croatia. In Italy, since the 2002 (Sfriso et al., 2002), a strong relationship between the Rhodophyta/ Chlorophyta ratio (R/C) and the environment ecological status was recorded and this index was employed for the assessment of both coastal waters and transitional systems. Concurrently, for transitional systems, a more precise methodology: the Macrophyte Quality Index (MaQI), both in an expert (E-MaQI) and rapid (R-MaQI) version was set up (Sfriso et al., 2007, 2009). In 2009 MaQI was accepted by Italy for the national transitional water assessment. At present an intercalibration exercise between the Mediterranean Geographycal Intercalibration Groups (Med-GIG) of each Mediterranean Member State is occurring by applying the national method of Greece (EEI) and the national method of Italy (MaQI). In this paper an example of their application in stations of different ecological status sampled in Venice Lagoon in 2008 is presented. Materials and methods – Fig. 1 shows the central part of the Venice Lagoon and the 5 sampling sites. Each station has a ray of 15-20 m and it includes both soft and hard substrata. Macroalgae have been recorded in June and October 2008 by SCUBA divers. Concurrently, total macrophyte coverage was determined. The coverage of the dominant taxa was obtained by sorting and weighting the dominant taxa of 3-6 samples recorded by a rake according to ISPRA sampling methodologies (ISPRA, 2008) and 68 A. Sfriso, C. Facca their successive integration which is under publication. The reference EQR values are 1.03 and 1.00 for euhaline and polyhaline stations, respectively (Sfriso et al., 2009). Fig. 1 - Central part of the Venice Lagoon and sampling stations. Assessment by MaQI application. Parte centrale della laguna di Venezia e stazioni di campionamento. Valutazione dello stato ecologico mediante l’applicazione dell’indice MaQI. Results – Total macrophytes ranged from 107 taxa (105 macroalgae and 2 angiosperms) at St. 1 (San Nicolò) to 17 taxa at St. 5 (Marco Polo Airport) (Tab. 1). The numbers are the sum of the taxa recorded in June and October and, obviously they are higher than each single sampling. Seagrasses were recorded only at St. 1 (San Nicolò) and at St. 2 (Alberoni Ottagono). The R/C ratio, ranged from 1.8 at St. 1 to 0.4 at St. 5. By normalising the values with the highest values recorded in the reference areas (2.21 and 2.00 for euhaline and polyhaline stations, respectively, Sfriso et al., 2009) the station assessment is “High” for St. 1, “Good” for Sts. 2 (Alberoni Ottagono) and 3 (Lido watershed), “Poor” for St. 4 (San Giuliano) whereas at station 5 (Marco Polo Airport) the index is not applicable because of the number of species is lower than 20. The results obtained by applying E-MaQI are similar to the R/C assessment, except at St. 3 (Lido watershed) where the classification results to be “Moderate”. However, the normalised scores obtained by the two indices are very close one to the other and to the boundary classes. Also E-MaQI is not applicable at St. 5 (Airport) because of the low number of taxa. On the contrary R-MaQI can be applicable also if macrophytes are quite missing and St. 5 (Marco Polo Airport), as expected, is assessed as “Bad”. For all the other stations the environmental assessment is the same of that obtained by E-MaQI. EEI is applicable only at Sts. 1, 2, 3 where macrophyte biomass was higher than 30%. However, the classification is the same only at St. 2 (Alberoni Ottagono) whereas the assessment of the other two stations differs even of two classes: St. 1 (S. Nicolò) is assessed as “Moderate” and St. 3 (Lido watershed) is assessed as “Bad”. In fact, that index is mainly based on macrophyte coverage whereas MaQI takes Macrophytes as biological element for the assessment and management of transitional water systems 69 into consideration mainly the presence of high score taxa and their relationship with some environmental parameters and pollutants. Tab. 1 - Check-List of macrophytes (macroalgae and angiosperms) recorded in some stations of the Venice Lagoon in June and October 2008 and indices of ecological status application. Lista delle macrofite (macroalghe e angiosperme) raccolte in alcune stazioni della laguna di Venezia in giugno ed in ottobre 2008 ed applicazione di indici di stato ecologico. Conclusions – Macrophytes are very sensitive to the ecological conditions of transitional waters and some indices can supply a very useful tool both in their monitoring and management. In fact, the presence/absence of high score taxa such as angiosperms and many macroalgae is strongly related to the environment trophic state and pollution level. Therefore, the preservation or restoring of angiosperm meadows should be the first objective for the transitional system management. 70 A. Sfriso, C. Facca References GIACCONE G., CATRA M. (2004) - Rassegna sugli indici di valutazione ambientale con macroalghe per definire lo stato ecologico delle acque costiere del Mediterraneo (Direttiva 2000/60/CE). Biol. Mar. Mediterr., 11 (1): 57-67. 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