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Temporal distribution of phytoplankton species composition and main environmental variables in Santa Giusta Lagoon (central-western Sardinia) = Distribuzione temporale della composizione specifica del fitoplancton e dei principali parametri ambientali ne

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A. LUGLlÈ, F. FIOCCA, G. CECCHERELLI, N. SECHI

TEMPORAL DISTRIBUTION OF PHYTOPLANKTON SPECIES

COMPOSITION AND MAIN ENVIRONMENT AL VARIABLES IN

SANTA GIUSTA LAGOON (CENTRAL-WESTERN SARDINIA)

DISTRIBUZIONE TEMPORALE DELLA COMPOSIZIONE SPECIFICA

DEL FITOPLANCTON E DEI PRINCIPALI PARAMETRI

AMBIENTALI NELLO STAGNO DI SANTA GIUSTA

(SARDEGNA CENTRO-OCCIDENTALE)

Estratto da:

BIOLOGIA MARINA MEDITERRANEA, Periodico edito dalla Societò Italiano di Biologia Morino

VoI. 8 • fase. 1 • 2001 (PARTE PRIMA) •

SHARM EL SHE/KH (13· 20 Maggio 2000)

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Biol. Mar. Medit. (2001), 8 (1): 332-337

A. LUGLlÈ, F. FIOCCA, G. CECCHERELLI, N. SECHI

Dipartimento di Botanica ed Ecologia Vegetale, Università di Sassari, Via F. Muroni 25, 07100 Sassari, Italia.

TEMPORAL DISTRIBUTION OF PHYTOPLANKTON SPECIES

COMPOSITION AND MAIN ENVIRONMENTAL VARIABLES IN

SANTA GIUSTA LAGOON (CENTRAL-WESTERN SARDINIA)

DISTRIBUZIONE TEMPORALE DELLA COMPOSIZIONE SPECIFICA

DEL FITOPLANCTON E DEI PRINCIPALI PARAMETRI

AMBIENTALI NELLO STAGNO DI SANTA GIUSTA

(SARDEGNA CENTRO-OCCIDENTALE)

Abstract

Water samp/es and environmenta/ data were examined at four stations at biweek/y or month/y interva/s, depending on the period, from February 1990 to December 1999. Phytop/ankton composition was estimated in these samp/es.

The abiotic parameters revea/ed a difference in environmenta/ conditions between the outer area of the /agoon and those closer to the coast. Phytop/ankton structure was quite consistent among different areas of the /agoon. Abso/ute abundance was very different among classes, with Ch/orophyceae much more abundant than Bacillariophyceae. Haptophyceae and Chrysophyceae were the /east represented classes. Density of classes reached peaks in different periods of the year, suggesting a recurrent pattern in taxa succession.

Key-words: coasta/ /agoons. phytop/ankton succession, species composition.

Introduction

Coastal lagoons are autonomous dynamic systems with a high productivity potential and a number of common geo-morphological and ecological features (Nixon, 1982). These areas have naturalisti c importance but also play a great economic role: in the Mediterranean, for example, more than a half of the larger lagoons are used for aquaculture (for both fish and shellfish) (Bacher et al.,

1995, Sorokin et al., 1999). In coastal lagoons dominant primary producers vary most1y in relation to morphological characteristics of the site, hydrodynamics and nutrient supply; depending on the c1imatic region in which they are located, different altemation in seasonal dominant component occurs (Knoppers, 1994). Santa Giusta Lagoon (Fig. l), the widest brackish basin of the west Sardinia (Italy), seems a macroalgal-based lagoon where the dominance of macroalgae (mainly Ulva spp.) and phytoplankton altemates depending mostly on life cycle characteristics of the former species and the successive nutrient recycling. In these last 15 years, the enhanced nutrient availability due to urban waters and industriaI discharges has caused marked changes in the environment, with a progressive increase in summer dystrophic crisis, macroalgal blooms and extensive fish mortality (Sechi et al., 2000).

In this paper we define the intra-annual dynamics of phytoplankton and the most important environment al parameters by analysing IO years data obtained through biweekly and monthly collection since 1990.

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Phytoplankton species composition in Santa Giusta lagoon 333

S. Giusta Lagoon

Fig. l - Santa Giusta Lagoon showing the sampling stations and its position in Sardinia.

La Laguna di Santa Giusta, stazioni di campionamento e localizzazione in Sardegna.

Materials and methods

Santa Giusta lagoon (39°52'N g036'E) has a surface area of about g km2 and a mean depth of l m. The lagoon is almost circular and choked, divided from the sea by a sandy barrier; it communicates with the sea mainly through Pesaria Channel (about 3 km long). Half-way down the Pesaria Channel, a fish catch system was built and it caused a considerable depth and width reduction, with heavy consequences on the tide exchange volume. Water exchange peri od was bimonthly, due to an inflow of 170 x 106 m3 y-I, whose 30 were freshwater.

Water samples and ambient physical and chemical data were examined at four stations at biweekly and monthly intervals, depending on the period, from February 1990 to December 1999. Station l, 2, 3 correspond to the inner areas while station 4 to the outer area.

Temperature and salinity were measured using a multiparameter probe Idronaut. For phytoplankton analysis, water samples were collected at surface (0.5 m depth) and fixed using 4% neutralised formalin. Other samples were transferred to the laboratory where total inorganic N (ammonium

+

nitrate

+

nitrite nitrogen), total

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334 A. LUGuÈ, F. FIOCCA, G. CECCHEREW, N. SEcm

P, reactive silica (Strickland and Parsons, 1972) and chlorophyll a (se OR-UNESeO, 1966) were measured. Phytoplankton composition was estimated following Utermohl method (1931).

Results

The lagoon was characterised by high nutrient concentrations (Fig. 2), with inorganic total N reaching peaks in winter and total P in February. Temporal fluctuations of these variables have shown lower concentrations in the middle

500 et) 400 'E Z300 Cl E 200 - o - st1 - D - st2 -.tr- sta ___ st4

Totallnorganic Nitrogen Total Phosphorus

300 250 3 200<.0 "'O 15031" 100 O~~~~~~~~~~~ 100 ~~~~~ __ ~~ ____ ~~~~50 35 30 25 20 15 10

Temperature Reactive silica

8 6 3 <.O 4 Q? 5~~~ ____ ~~~--~~~~~ 45 40 35 30 25 20 Salinity Chlorophyll5! 30 25 20 3 15 (Q 3 10 ÙJ 15 5 10 O J F M A M J J A S O N D J F M A M J J A S O N D

Fig. 2 - Temporal distributions of abiotic data (temperature, salinity, reactive silica, total inorganic

N, total P, Chlorophyll a) in each station: monthly means and SE were calculated from

lO years of data (1990-1999).

Fluttuazione temporale dei parametri abiotici (temperatura, salinità, silice, N totale inor-ganico, P totale, clorofilla a) in ogni stazione: le medie mensili e l'ES sono state calcolate dai dati raccolti in 10 anni (1990-1999).

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Phytoplankton species composition in Santa Giusta lagoon 335

area of the lagoon than in the coastal area. Reactive silica great1y increased in summer; values relative to the outer part did not undergo seasonal fluctuations. Clear seasonal fluctuations were evident for water temperature and salinity, as expected. Slightly different values were observed for the outer station that probably is more influenced by marine conditions. Chlorophyll a also fluctuated greatly during the year, showing maximum values in J anuary sharply decreasing unti l ApriI and increasing again during summer. In autumn chlorophyll a concentration was very low, in the whole lagoon.

Phytoplankton dynamics was c1ass-specific since peaks relative to each taxon occurred in different periods of the year (Fig. 3). The species responsible for peaks within the single classes often change depending on the year, except for Chlorophyceae for which the abundance of Chlorella sp. always determined the greatest density. Chlorophyceae dominated with high densities during the first months of the year, when nutrient supply was high and temperature and salinity were low. Bacillariophyceae showed higher density during J anuary and August; the latter peak corresponded to high concentration of reactive silica. The other classes showed short peaks that occurred mostly during summer and early autumn.

Discussion

The abiotic parameters evidenced that in Santa Giusta Lagoon a difference occurs in ambient condition between the outer area of the lagoon and the ones c10ser to the coast. This feature suggests that the former area is more influenced by marine conditions and the latter ones are more influenced by fresh water discharges. Overall environrnental conditions indicate the high trophic status of the lagoon and rapid variations in nutrient concentration, salinity and temperature.

Phytoplankton structure was quite consistent among areas of the lagoon, suggesting that good mechanisms of homogenisation operate at the site. Absolute abundance was very different among c1asses, being Chlorophyceae much more abundant than Bacillariophyceae. Haptophyceae and Chrysophyceae were the least represented classes.

Density of classes reached peaks in different periods of the year, suggesting a trend in taxa successione Winter and summer maximum values correspond to periods of high nutrient availability, in the former period because of high rainfall and consequent freshwater supply from the catchment area next to the lagoon, and in the latter period because of macroalgae decomposition.

Riassunto

In questo studio è stata esaminata la distribuzione temporale dei maggiori gruppi di microalghe e dei parametri ambientali dal febbraio 1990 al dicembre 1999. Con cadenza quindicinale o mensile, a seconda del periodo, sono stati prelevati campioni d'acqua in 4 stazioni nell'ambito della laguna sia per la determinazione delle caratteristiche ambientali che per l'analisi del fitoplancton.

L'andamento dei parametri ambientali considerati ha evidenziato una differenza tra l'area lagunare più esterna e quelle più vicine alla costa. Nonostante ciò la struttura del fitoplancton è risultata abbastanza uniforme tra le stazioni della laguna. L'abbondanza assoluta è molto diversa tra classi. Le Chlorophyceae sono state molto più abbondanti delle altre classi. Le Haptophyceae e le Chrysophyceae sono le classi meno rappresentate. La densità delle classi ha raggiunto picchi di abbondanza in differenti periodi dell'anno suggerendo un andamento ricorrente nella successione dei taxa.

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336 A. LUGuÈ, F. FIOCCA, G. CECCHEREW, N. SECHI

16000

Mean density (cells 103 l'l)

--<>- st1 - O - st2 - . - s13 ___ st4 2000 12000 Bacillariophyceae Cryptophyceae 1500 8000 1000 4000 500 O~~ __ ~~~~~~~~~~~!§~~~~~~~O 1000000 3000 Chlorophyceae 750000 2250 500000 1500 250000 750 0~~~T-~'-~~~~~~ _______ -4~~~~~~~~ __ ~0 100 2400 75 1800 50 1200 25 600

o-'--___

~

...

~~~

...

..._t ... ~~~!!~~~~~J_O 800 10000 600 7500 400 5000 200 2500 o~~~~~~~~~~~~ __ ~~~~~~~~=-~~O 8000 480000 Cyanophyceae 6000 360000 4000 240000 2000 120000 J F M M J J A S O N D J F M A M J J A S O N D

Fig. 3 - Temporal distributions of phytopIankton density of principI e taxonomic groups in each station of Santa Giusta Lagoon. Bacillariophyceae, Chlorophyceae, Haptophyceae, Chrysophyceae, Euglenophyceae, Cryptophyceae, Raphydophyceae, Dinophyceae, Ultraplankton, Cyanophyceae monthly means and SE were calculated from IO yeas (1990-1999) data (n=12-15).

Fluttuazione temporale della densità delle principali classi di fitoplancton in ogni stazione dello Stagno di Santa Giusta. Le medie mensili e l'ES per Bacillariophyceae, Chlorophyceae, Haptophyceae, Chrysophyceae, Euglenophyceae, Cryptophyceae, Raphydophyceae, Dinophyceae, Ultraplancton, Cyanophyceae sono state calcolate dai dati raccolti in IO anni (1990-1999) (n=12-15).

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Phytoplankton species composition in Santa Giusta lagoon 337

References

BACHER C., BIOTEAU H., CHAPELLE A. (1995) - Modelling the impact of a cultivated oyster population on the nitrogen dynamics: the Thau Iagoon case (France). Ophelia, 42: 29-54. KNOPPERS B. (1994) - Aquatic primary production in coastal Iagoons. In: Kjerfve B. (ed.)

Coastal lagoon processes, Elsevier Science PubIishers: 243-286.

NIXON S.W. (1982) - Nutrient dynamics, primary production and fishery yeIds Iagoons.

Oceanologica Acta, special voI., Actes Symposium International sur Ies Lagunes Cotieres, SCORlIABO/UNESCO: 357-381.

PINCKNEY J.L., MILLIE D.F., VINYARD B.T., PAERL H.W. (1998) - Environmental controIs of phytopIankton bloom in the Neuse River Estuary, North Carolina, USA. Can. J. Fish.

Aquat. Sci., 54: 2491-2501.

S.C.O.R.- UNESCO (1966) - Determination of photosynthetic pigments in sea water. Monograph

on Oceanographic Methodology: 1-64.

SECHI N., FIOCCA F., SANNIO A., LUGLIÉ A. (2000) - Santa Giusta lagoon (Sardinia): phytopIankton and nutrients before and after waste water diversion. Journal oi Limnology, In presso

SOROKIN Y.I., SOROKIN P.Y., RAVAGNAN G (1999) - AnaIysis of Iagoonal ecosystems in the Po River Delta associated with intensive aquaculture. Estuarine Coastal and Shelf Science, 48: 325-341.

STRICKLAND J.D.H., PARSONS T.R. (1972) - A praticaI handbook of seawater anaIysis. Fisheries Research board of Canada.

UTERMOHL H., (1931) - Neue Wege in der quantitativen Erfassung des PIanktons (mit besonderer Berucksichtigung des Ultraplanktons. Vero int. Vero theor. Angew. Limol., 5: 567-596.

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