COASTAL MARINE WATERS – BIOLOGICAL QUALITY ELEMENT CHLOROPHYLL a

    Panel 1
    Data aggiornamento scheda
    Autori

    Patrizia Borrello, Emanuela Spada

    Abstract
    Grafici interattivi
    Abstract

    The "chlorophyll" parameter is the only direct indicator of phytoplankton biomass available and has taken on the role of a metric for classifying ecological status according to the Biological Quality Element (BQE) – Phytoplankton in coastal waters (Ministerial Decree 260/2010). Chlorophyll is particularly sensitive to changes in trophic levels determined by nutrient (N and P) inputs from catchment basins flowing into the coastal area.
    In 2020, high status was recorded in 71.4% of cases, good status in 12.3%, and sufficient status in 16.2%. A general improvement in status was observed in Campania and Marche, while Emilia-Romagna and Sardinia saw a worsening. Marche, Liguria, and Abruzzo maintained all stations at high status.

    Descrizione

    Chlorophyll a is a primary indicator of phytoplankton biomass. As such, it is sensitive to changes in trophic levels determined by nutrient (N and P) loads from catchment basins affecting the examined coastal area. The chlorophyll parameter is commonly measured fluorometrically, using a multiparameter probe. This allows the measurement results to be graphically presented as vertical profiles along the water column.
    The availability of nutrients, in their dissolved mineral form, elicits a response from the coastal ecosystem in terms of increased primary production. The key role of the chlorophyll a parameter is to document this increase.
    In this sense, chlorophyll a ceases to be merely the photosynthetic pigment contained in the chloroplasts—organelles present in every phytoplankton cell—and becomes the most important of the trophic indicators. Although the functional relationships between chlorophyll and autotrophic phytoplankton biomass (in terms of cell count per liter, weight, etc.) are complex, this parameter is nonetheless the only directly measurable and widely monitored indicator of phytoplankton biomass in coastal water quality control programs.

    In accordance with Legislative Decree 152/2006 and subsequent amendments, the classification used to represent the indicator is based on the water body's typology. Specifically:

    • For macrotype 1 (coastal sites heavily influenced by freshwater inflows), the “chlorophyll a” value is calculated using the geometric mean.
    • For macrotypes 2 and 3 (moderately influenced or not influenced by freshwater inflows), the 90th percentile of the normalized data distribution is used.

    The high/good class threshold for macrotypes 1 and 2 is 2.4 mg/m³, while for macrotype 3 it is 1.1 mg/m³.
    The good/sufficient class thresholds are 3.5, 3.6, and 1.8 mg/m³ for macrotypes 1, 2, and 3, respectively.

    Scopo

    To assess the ecological status of coastal waters based on the BQE Phytoplankton, in accordance with Legislative Decree 152/2006 and subsequent amendments. This allows for the setting of quality objectives to be maintained and/or achieved. Spatial analysis of the indicator enables the establishment of relationships between nutrient loads in coastal systems and their response in terms of phytoplankton biomass production.
    Time series analysis of chlorophyll a data also enables monitoring of the effectiveness of strategies and actions taken for nutrient control and removal.

    Rilevanza
    È di portata nazionale oppure applicabile a temi ambientali a livello regionale ma di significato nazionale
    È in grado di descrivere la tendenza senza necessariamente fornire una valutazione della stessa.
    È semplice, facile da interpretare.
    È sensibile ai cambiamenti che si verificano nell'ambiente e/o nelle attività umane
    Fornisce un quadro rappresentativo delle condizioni ambientali, delle pressioni sull'ambiente e delle risposte della società.
    Fornisce una base per confronti internazionali.
    It has a threshold or reference value against which it can be compared.
    Solidità
    È basato su standard nazionali/internazionali e sul consenso nazionale/internazionale circa la sua validità
    È ben fondato sul piano tecnico e scientifico.
    Presenta affidabilità e attendibilità dei metodi di misurazione e raccolta dei dati
    Comparabilità nel tempo
    Comparabilità nello spazio
    Misurabilità (dati)
    Adeguatamente documentati e di fonte nota
    Aggiornati a intervalli regolari e con procedure affidabili
    Facilmente disponibili o resi disponibili a fronte di un ragionevole rapporto costi/benefici
    Un’ “adeguata” copertura spaziale
    Principali riferimenti normativi e obiettivi

    Legislative Decree 152/2006 and subsequent amendments. In accordance with Legislative Decree 152/2006, which mandates biological monitoring per Directive 2000/60/EC and Ministerial Decree 260/2010, which defines the ecological status classification criteria, every surface water body, including coastal waters, must achieve and maintain “good” environmental quality status by 2015.

    DPSIR
    Stato
    Risposta
    Tipologia indicatore
    Descrittivo (A)
    Riferimenti bibliografici

    Devlin, M., Best, M., Coates, D., Bresnan, E., O'Boyle, S., Park, R., Silke, J., Cusack, C. & Skeats, J. (2007). Establishing boundary classes for the classification of UK marine waters using phytoplankton communities. Marine Pollution Bulletin 55: 91-103. Giovanardi, F., Finoia, M.G., Russo, S., Amori, M. and B. Di Lorenzo, 2006. Coastal waters monitoring data: frequency distributions of the principal water quality variables. J. Limnol., 65(2): 65-82 Giovanardi, F. and E. Tromellini, 1992. Statistical Assessment of Trophic Conditions. Application of the OECD Methodology to the Marine Environment. Proc. Int. Conf. Marine Coastal Eutrophication. Sci. Total Environ. Suppl. 1992: p. 211-233. OECD – Vollenweider, R.A. and J.J. Kerekes Eds, 1982. Eutrophication of Waters, Monitoring, Assessment and Control-O.E.C.D.-Paris. WFD Intercalibration Phase 2: Milestone 5 report, 2011

    Fonte dei dati

    Coastal ARPA

    Frequenza di rilevazione dei dati
    6 volte nell'arco di un anno
    Accessibilità dei dati di base

    The basic information is accessible through the SINTAI system - http://www.sintai.sinanet.apat.it/ used by coastal ARPA to transmit data using shared information standards at national level.

    Copertura spaziale

    Anno 2018: Coastal regions 12/15 Anno 2019: Coastal regions  11/15 Anno 2020: Coastal regions 14/15

    Copertura temporale

    2018-2019-2020

    Descrizione della metodologia di elaborazione

    Within the framework of the works for the Intercalibration of the methods and classification criteria related to the BQE (Biological Quality Element) phytoplankton, as provided by Directive 2000/60 WFD, the Member States belonging to the Mediterranean Eco-Region have mainly adopted two types of metrics based on chlorophyll a: the value of the 90th percentile for distributions of chlorophyll a normalized through logarithmic transformation and referring to a period of at least 5 years, and the value of the geometric mean, calculated over a period of at least one year. For further details, reference is made to the technical annex of the Classification Decree (Ministerial Decree Environment 260/2010).
    In accordance with what is provided in Legislative Decree 152/2006 and subsequent amendments and additions, the classification to represent the indicator is carried out based on the type of water body. In particular, for macrotype 1, corresponding to coastal sites strongly influenced by inputs of continental freshwater, the value of “chlorophyll a” is calculated using the geometric mean. For the types included in macrotopes 2 and 3, corresponding respectively to coastal sites moderately influenced or not influenced by inputs of continental freshwater, the 90th percentile is considered for the normalized distribution of data for the calculation of the “chlorophyll a” value.
    The high/good class boundary limit for macrotopes 1 and 2 is 2.4 mg/m³, while it is 1.1 mg/m³ for macrotype 3; the good/moderate class boundary limits are 3.5, 3.6, and 1.8 mg/m³ for macrotopes 1, 2, and 3 respectively.

    Periodicità di aggiornamento
    Annuale
    Data quality

    In general, the information quality regarding this indicator is good and consistent with other available data for the coastal areas studied (e.g., riverine input, salinity variation, nutrient concentrations). The indicator is easily measurable, thanks to well-established chlorophyll a monitoring methods. The comparison with regulated quality classes in Legislative Decree 152/2006 ensures its relevance for the classification of marine-coastal water bodies under the Water Framework Directive 2000/60/EC and the six-year River Basin Management Plans.
    The relationship between chlorophyll a concentration and eutrophication has been extensively studied since the 1970s, and the choice of this metric is backed by a broad scientific literature, ensuring high scientific robustness.

    Stato
    Medio
    Trend
    Non definibile
    Valutazione/descrizione dello stato

    In 2020, high status was recorded in 71.4%, good status in 12.3%, and sufficient status in 16.2% of stations (Table 1, Figure 1). Campania and Marche saw general improvements, while Emilia-Romagna and Sardinia worsened. Friuli Venezia Giulia remained stable. Liguria, which nearly doubled its stations, along with Marche and Abruzzo, had all stations in high status. Stations classified as high and good totaled about 88.5%, but the increase in stations with sufficient status prevented achievement and maintenance of “good” environmental quality status.

    Trend

     

    Valutazione/descrizione del trend

    In 2018, 72% of coastal stations across 12 reporting regions were in high status, 20% in good, and 8% in sufficient status. In 2019, high status stations reached nearly 80%, good status dropped to 11.3%, and sufficient status decreased to 4%, favoring the high status category. In 2020, there was a slight decline in high status (71.4%), a slight increase in good status (12.3%), and a notable increase in sufficient status (16.2%) compared to previous years.

    Commenti

    The processed data (Table 1) refer only to stations from regions that formally and completely submitted ecological status classification information for the BQE Phytoplankton in Coastal Waters to SINTAI. Each region reports its stations classified on a “high – good – sufficient – poor – bad” scale based on the “chlorophyll a” index value, considering the macrotipo of the water body each station belongs to.
    From 2018 to 2020, despite a decrease in the number of stations, there was an increase in stations rated sufficient (from 23 to 42) (Table 1 and Figure 1). The sufficient status rating mainly pertains to Sicily, Sardinia, and the northern Adriatic coast (Emilia-Romagna), which belongs to macrotipo I (High Stability). For the latter, the direct role of the Po River and other catchments flowing into the northern Adriatic in maintaining high trophic levels is confirmed.
    As for Sicily and Sardinia, the cause is likely nutrient inputs from smaller rivers, which can locally elevate trophic levels.
    For the Tyrrhenian coastal regions, from 2018 to 2020, there was a clear improvement in Lazio and Campania. Lastly, the significant percentage of stations in high status is consistent with the general oligotrophic nature of Tyrrhenian coastal waters (Table 1).

    Grafici interattivi
    Allegati
    Titolo

    Table 1: Number of stations by quality classes - Organic Quality EQB Fitoplancton Chlorophylla a

    Fonte

    ISPRA processing on data from coastal ARPA

    Legenda

    /data not received

    Thumbnail
    Titolo

    Figure 1: Classification EQB Fitoplankton - Chlorophyll a (2020)

    Fonte

    ISPRA processing on ARPA data

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