• Non ci sono risultati.

Il rapporto dell'Agenzia Europea per l'Ambiente sulle acque di balneazione - SNPA - Sistema nazionale protezione ambiente

N/A
N/A
Protected

Academic year: 2022

Condividi "Il rapporto dell'Agenzia Europea per l'Ambiente sulle acque di balneazione - SNPA - Sistema nazionale protezione ambiente"

Copied!
7
0
0

Testo completo

(1)

Country report

June 2020

Italian bathing water quality in 2019

Italy

(2)

Bathing water quality in the 2019 season

Italy

Under the provisions of the Bathing Water Directive, more than 21 000 bathing waters are monitored in Europe each season. The monitoring data and other information regarding bathing water management are reported to the European Environment Agency by 30 European countries. These are then assessed for the annual European Bathing water report (European Bathing Water Briefing by 2020), published by the EEA, and more detailed national reports.

1. Bathing Water Directive reporting in the 2019 season

Bathing waters are quality classified according to two microbiological parameters (Escherichia coli and Intestinal enterococci) defined in the Bathing Water Directive. A total of 96.8% of reported bathing waters are in line with the minimum quality standards of the Directive and are thus classified as ‘sufficient or better. 97 bathing waters are classified ‘poor .

More information is available at the national bathing water portal:

http://www.portaleacque.salute.gov.it/PortaleAcquePubblico/homeBalneazione.do Bathing waters in the 2019 season

Total reported 5535

Coastal 4864

Inland 671

First identified in 2019 19

Delisted in 2019 25

Total reported samples 36612

Bathing water quality in the 2019 season

Excellent 4894 (88.4%)

Good 326 (5.9%)

Sufficient 140 (2.5%)

Poor 97 (1.8%)

Not classified 78 (1.4%)

(3)

2. Bathing Water Directive monitoring

Each bathing water identified by the reporting country must have a monitoring calendar, established before the bathing season. The monitoring calendar requirements can be summarised as follows: (1) a pre-season sample is to be taken shortly before the start of each bathing season; (2) no fewer than four (alternatively, three in specific cases) samples are to be taken and analysed per bathing season; and (3) an interval between sampling dates must never exceed one month.

From the reported data, the assessment also designates effective implementation of the monitoring calendar (Table 1).

Table 1: Bathing waters in 2019 according to implementation of the monitoring calendar

Count Share of total (%) Monitoring calendar implemented

A bathing water satisfies the monitoring calendar conditions listed above.

5160 93.20

Monitoring calendar not implemented

A bathing water does not satisfy the monitoring calendar conditions listed above. It may be quality-classified if enough samples are available in the last assessment period.

375 6.80

In addition to the monitoring calendar, management specifics of the last assessment period are also assessed.

The resulting status primarily indicates whether the complete dataset for the four seasons is available, but also explains why the bathing waters do not have the complete dataset for the last assessment period. The latter may indicate developing conditions at the site most importantly, whether the bathing water has been newly identified within the period, or whether any changes have occurred that are likely to affect the classification of the bathing water.

Table 2: Management specifics in the last assessment period, 2016-2019

Count Share of total (%) Continuously monitored

A bathing water has been monitored in each bathing season in the last assessment period.

5427 98.00

Newly identified

A bathing water was identified for the first time within the last assessment period. Such status is assigned for the full four years after being reported.

60 1

Quality changes

A bathing water was subject to changes described in Bathing Water Directive Article 4.4 within the last assessment period.

Such status is assigned for the full four years after being reported.

12 0.20

Monitoring gap

A bathing water was not monitored for at least one season in

36 0.70

(4)

3. Bathing water quality

3.1 Coastal bathing waters

Coastal bathing waters are situated on the sea or transitional water coastline, with the respective parameter thresholds defined in Annex I of the Directive. They are subject to more strict thresholds than inland bathing waters. The quality trend for the period 1990 2019 (if historical data are available) is shown in Figure 1. The number of bathing waters by quality class for the last assessment period, 2016 2019, is given in Annex I Bathing water quality, 2016-2019.

Figure 1: Trend in coastal bathing water quality

Notes: Each column represents an absolute number of bathing waters in the season. The ‘good and ‘sufficient quality classes are merged for comparability with the classifications under the preceding Bathing Water Directive 76/160/EEC.

0 1000 2000 3000 4000 5000 6000

1990 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014 2015 2016 2017 2018 2019

Number of bathing waters

Not classified Poor Good or sufficient Excellent

(5)

3.2 Inland bathing waters

Inland bathing waters are situated at fresh water rivers and lakes that have the respective parameter thresholds as defined in Annex I of the Directive. The quality trend for the period 1990 2019 (if historical data are available) is shown in Figure 2. The number of bathing waters by quality class for the last assessment period, 2016 2019, is given in Annex I Bathing water quality, 2016-2019.

Figure 2: Trend in inland bathing water quality

Notes: Each column represents an absolute number of bathing waters in the season. The ‘good and ‘sufficient quality classes are merged for comparability with the classifications under the preceding Bathing Water Directive 76/160/EEC.

0 100 200 300 400 500 600 700 800

1990 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014 2015 2016 2017 2018 2019

Number of bathing waters

Not classified Poor Good or sufficient Excellent

(6)

Annex I Bathing water quality, 2016–2019

Table 3: Bathing water quality by water category and season

Total count of bathing

waters

Excellent Good Sufficient Poor Not classified

Count % Count % Count % Count % Count %

Coastal

2016 4864 4414 90.7 237 4.9 75 1.5 95 2.0 43 0.9

2017 4864 4373 89.9 253 5.2 88 1.8 75 1.5 75 1.5

2018 4871 4382 90.0 251 5.2 102 2.1 79 1.6 57 1.2

2019 4864 4290 88.2 292 6.0 126 2.6 90 1.9 66 1.4

Inland

2016 654 599 91.6 31 4.7 9 1.4 5 0.8 10 1.5

2017 667 599 89.8 31 4.6 16 2.4 4 0.6 17 2.5

2018 668 605 90.6 28 4.2 14 2.1 10 1.5 11 1.6

2019 671 604 90.0 34 5.1 14 2.1 7 1.0 12 1.8

Total

2016 5518 5013 90.8 268 4.9 84 1.5 100 1.8 53 1.0

2017 5531 4972 89.9 284 5.1 104 1.9 79 1.4 92 1.7

2018 5539 4987 90.0 279 5.0 116 2.1 89 1.6 68 1.2

2019 5535 4894 88.4 326 5.9 140 2.5 97 1.8 78 1.4

(7)

Annex II Bathing water quality map

Riferimenti

Documenti correlati

3 Valore pari al 30% dello standard di qualità di 0.1 µg/L per la singola sostanza, come richie- sto dalla direttiva 2009/90/CE, che stabilisce le specifiche tecniche per

Prima dell’inizio della stagione balneare, la Regione ne stabilisce la durata ed individua il calendario di monitoraggio, le cui  date  sono  distribuite  con 

• Fornire un quadro robusto, che possa proporre raccomandazioni ai decisori politici sui regolamenti ambientali, oltre che una metodologia di valutazione degli impatti per chi

Il presente rapporto illustra i risultati relativi alle attività di monitoraggio delle acque destinate alla balneazione della Regione Marche svolte da ARPA Marche

I dati della Sicilia non comprendono le province di AG, CT, ME, (Decreto Assessorato Salute Regione Sicilia 19 marzo 2020), per le quali non è stato possibile reperire la

ISPRA E LE AGENZIE AMBIENTALI COSTIERE HANNO COSTITUITO UN GRUPPO DI LAVORO PER LA STESURA DI LINEE DI INDIRIZZO PER LO STUDIO DELL’AREA D’INFLUENZA AI FINI DELLA GESTIONE DELLE

Nelle tabelle non sono considerate le aree di balneazione di nuova istituzione o ancora “non classificate”, così come non sono presenti le aree in cui ci sono divieti di

Questo indicatore segnala il livello di contaminazione totale alfa nelle acque dell’invaso del Pertusillo Come valore di riferimento si assume il livello di