The tide is a periodic phenomenon of rising and falling sea levels caused by the gravitational attraction exerted by the Moon, the Sun, and other celestial bodies on the Earth's water masses, and secondarily by meteorological disturbances. Data from the National Tide Gauge Network (ISPRA) were used to characterize the amplitude of the astronomical component of the tidal signal along Italian coasts. As well known, astronomical tides vary significantly across the different Italian seas, reaching their maximum range in the Northern Adriatic and Venice Lagoon, being strongly influenced by the basin's configuration.

A continuous monitoring over time of the variations of the astronomical tidal amplitude allows to highlight the hydrodynamic and therefore morphological changes inside the Venice Lagoon, which owes its survival to the maintenance of delicate environmental balances. The width of the tide in the lagoon is compared with the characteristic one of the Gulf of Venice, belonging to the same area from a geological point of view, but exempt from the anthropic intervention that distinguishes the transition environment considered. The tidal height trend is now substantially stable throughout the lagoon, after the strong variations observed as a result of profound changes introduced to the lagoon morphology during the first decade of the century.

The quality of bathing waters is fundamental for safeguarding citizens' health and also plays an important role from the perspective of protecting the natural environment and in terms of economic aspects in the tourism sector. For this reason, specific monitoring is carried out throughout the entire bathing season.
For the 2023 bathing season, more than 31,000 samples of sea and lake water were collected and analyzed over a total of more than 5,000 km of coastline designated for bathing.
At the municipal level, the kilometers of coastline are divided into more or less extensive bathing waters, for a total of 5,490 bathing waters.
The results of the analyses, in addition to ensuring the absence of health and hygiene risks during the season, also made it possible to classify the waters.
The classification was made using the monitoring results from the 2023 bathing season and those of the previous three seasons (2022-2021-2020).
At the national level, most of the waters fall into the excellent class (90.6%), however, critical issues still persist due to the presence of waters in the poor class (1.3%) and not classifiable (0.5%), for which it is not possible to express a quality judgment.
Also at the regional level, the percentage of waters in the excellent class is the highest and in some cases equals 100%.
In almost all regions, the waters in the sufficient and poor classes are decreasing, but the presence of the latter still prevents the full achievement of the directive’s objective.

Any solid material, manufactured or processed by humans, abandoned or lost in the marine and coastal environment or that reaches the sea in any way is defined as marine litter. Italy, with Legislative Decree No. 190/2010 transposing the Marine Strategy Framework Directive, has been conducting an intensive marine litter monitoring program since 2015, including beach litter. Twice a year, in spring and autumn, the coastal Regional Environmental Protection Agencies (ARPA) carry out monitoring of solid waste present in sample areas of 69 reference beaches along the national coastline. To assess the cleanliness of the beaches based on the density of litter present in the monitored sample areas, the Clean Coast Index (CCI) was calculated, an indicator developed and applied internationally.

In 2023, the CCI was calculated for 69 beaches both in spring and autumn. In spring, 80% of the monitored beaches were clean or very clean compared to 12% of dirty or very dirty beaches. In autumn, 77% of the beaches were clean or very clean, while 12% were dirty or very dirty. The rest of the beaches were fairly clean. Compared to the previous year, the percentage of clean or very clean beaches increased in autumn (75% in 2022), while in spring it remained the same.

Ostreopsis cf. ovata is a potentially toxic benthic microalga, currently present in most Italian coastal regions with blooms that can lead to human intoxication phenomena and toxic effects on benthic marine organisms (states of distress or mortality). The continuous expansion along the Italian coasts of Ostreopsis cf. ovata, of its blooms and the associated health, environmental and economic issues, has led to the establishment of a monitoring surveillance program of the microalga starting from 2007. This activity is carried out annually in the summer season by the Regional Environmental Agencies (ARPA). The data so far provided by the ARPA, collected and processed by ISPRA, have clarified the distribution and trend of blooms at national and regional level. To date, the microalga has been detected at least once in the monitoring campaigns carried out so far in 12 out of 15 coastal regions. In 2023, Ostreopsis cf. ovata is present in 12 coastal regions, that is in 145/221 stations (68.7%), while it is absent in all samples taken along the coasts of Emilia-Romagna, Molise and Veneto.

A continuous monitoring over time of changes in the delay in the propagation of the astronomical tide allows to highlight the hydrodynamic and therefore morphological changes inside the Lagoon of Venice, which owes its survival to the maintenance of delicate environmental balances. The tidal propagation delays within the lagoon are calculated with respect to the Gulf of Venice, belonging to the same area from a geological point of view, but exempt from the anthropic intervention that distinguishes the lagoon environment considered. Tidal propagation delays are greater the greater the distance of the observation point from the port mouth from which it is fed. The tidal wave takes about 35/40 minutes to enter the lagoon through the narrowing of the three port mouths, while it takes about three hours to reach the most inland and remote areas.

Eutrophication is a process caused by the enrichment of nutrients, particularly nitrogen and phosphorus compounds, which leads to an increase in primary production and algal biomass, resulting in the alteration of benthic communities and, in general, a decline in water quality. The input of nitrogen and phosphorus into the marine and coastal environment can originate from diffuse sources (river loads, major collectors of agricultural activity, and urban discharges) and point sources (discharges from wastewater treatment plants, industrial activities, and aquaculture operations). Objectives related to eutrophication control and management are set by the Water Framework Directive (WFD, Directive 2000/60/EC), the Marine Strategy Framework Directive (Descriptor 5, Directive 2008/56/EC), and the Nitrates Directive (Directive 91/676/EEC) and Urban Waste Water Treatment Directive (Directive 91/271/EEC), which are particularly focused on pressure management. The causes of eutrophication are primarily linked to nutrient inputs carried into the sea by rivers or coastal settlements, which cause serious negative impacts on the health of marine ecosystems and the sustainable use of goods and services. The main sources of nutrients are related to the agri-livestock and urban sectors.

Environmental assessments regarding eutrophication, in accordance with the requirements of Directive 2008/56/EC, have highlighted the achievement of Good Environmental Status. Therefore, the measures adopted so far under Directive 2000/60/EC, Directive 91/676/EEC, and Directive 91/271/EEC have proven effective in achieving environmental targets.

The monitoring provided by the Marine Strategy Framework Directive 2008/56/EC for Descriptor 7 considers the permanent alterations of hydrographic conditions due to coastal and marine infrastructures subject to national EIA, constructed or under construction or design since 2012. The reference indicator for D7C1 relates to the extent of coastal marine water bodies in each marine subregion, defined under Directive 2000/60/EC, which presents impacts due to permanent changes in hydrographic conditions due to new infrastructures constructed since 2012 and subject to national EIA. The objective for this indicator is not to exceed 5% of the extent of coastal marine water bodies. In 2023, the objective was achieved.

Italy, in application of the Marine Strategy Framework Directive, has implemented an extensive marine litter monitoring program since 2015, including micro-litter present in the surface layer of the water column. This monitoring is conducted by the National System for Environmental Protection (of which ISPRA is a part), under the coordination of the Ministry of Environment and Energy Security (MASE). The composition, quantity, and distribution of surface micro-litter are essential parameters for achieving the good environmental status of marine waters, the objective of the Directive. Micro-litter are particles smaller than 5 mm, whose origin is difficult to identify once dispersed in the environment. These particles derive from both primary sources, such as pellets and microbeads used in cosmetics or abrasive products, and secondary sources, such as the fragmentation of macro-litter. With the data processing carried out from 2016 to 2022, it was possible to define a median density value of micro-particles present in our seas, equal to 0.04 micro-particles per m², or 40,000 micro-particles per km². This value is confirmed by adding the 2023 data to the series. At the Mediterranean level, the Barcelona Convention has set a threshold value of 0.000845 micro-particles per m² (845 micro-particles per km²), therefore, compared to this value, Italy is still far from achieving good environmental status.

The Marine Strategy (Directive 2008/56/EC) represents an important governance tool for the marine system, promoting the adoption of strategies aimed at safeguarding the marine ecosystem to achieve Good Environmental Status. Good Environmental Status is assessed based on 11 themes or qualitative descriptors, and among these, Descriptor 10 requires that the properties and quantities of marine litter do not cause harm to the coastal and marine environment. Since 2015, Italy has been implementing an extensive monitoring program for marine litter, including beach litter. In 2023, the median of total marine litter stranded on Italian shores was 250 items per 100 m, the lowest value in the entire historical series. However, this is still a density significantly higher than the threshold value of 20 items per 100 m, established at the European level as a requirement for achieving Good Environmental Status. As in previous years, single-use plastics are the most common type of beach litter, representing 13% of the total; however, for this type of litter, there is a sharp decline compared to 2022 (29%), which, if confirmed in the coming years, could represent a significant first result of the effectiveness of the Marine Strategy Measures Program and, in particular, the application of Directive 2019/904 for the reduction of single-use plastics.

Descriptor 8 of the Marine Strategy Framework Directive 2008/56/EC (MSFD), in order to achieve good environmental status of marine waters through the gradual elimination of pollution, specifically requires the assessment of the presence of chemical contaminants and their effects in environmental matrices. During the 2021–2023 period, ISPRA conducted monitoring of the Adriatic Sea Subregion (MAD), Ionian Sea and Central Mediterranean Subregion (MIC), and Western Mediterranean Subregion (MWE). The data were processed and integrated with those provided by regional agencies and experimental zooprophylactic institutes.

This monitoring revealed that, although the data coverage for the study of contaminant concentrations varied across matrices and subregions, there was an overall improvement. This allowed for the assessment of GES (Good Environmental Status) for the sediment matrix in two MRUs and for the biota matrix in the Adriatic MRU.

The percentage of treated wastewater reflects the amount of biodegradable organic load that reaches urban wastewater treatment plants compared to the total organic load produced by agglomerations (2,000 PE or more) across the national territory. In 2022-2023, this percentage is 93.51%, an increase compared to 2020 (93.3%).

Upwelling is a physical phenomenon caused by the action of wind and currents that can generate an upwelling current, oriented offshore and perpendicular to the coast. This phenomenon has a significant impact on the local fish fauna and is therefore of great interest. The identification of the most favorable areas for the occurrence of this phenomenon has been carried out using wind speed and direction data provided by the National Tide Gauge Network (RMN) managed by ISPRA. These data, appropriately processed, allow the identification of coastal areas that are most likely to be exposed to the upwelling phenomenon, such as the Carloforte area in Sardinia, which is confirmed to be among the most favorable for the generation of this variable.

The presence or absence of a sewage network and the percentage of wastewater conveyed into collection systems indicate the degree of compliance with the requirements of the applicable regulations. In 2022-2023, the national compliance rate is 99.1%. Of the organic load, 95.7% is conveyed into the sewer system, 3.6% is treated through individual systems, while 0.7% is not connected.

Compliance monitoring allows for an understanding of the technological adaptation status of urban wastewater treatment systems for agglomerations greater than or equal to 2,000 PE (Population Equivalent). This is particularly useful for planning potential actions aimed at water protection.

Between 2022 and 2023, out of the 3,037 agglomerations analyzed, approximately 77% were found to be compliant, 13.8% non-compliant, 4.6% partially compliant, and 4.6% with data unavailable. A 100% compliance rate is recorded in Piedmont, Emilia-Romagna, Umbria, and the Autonomous Provinces of Trento and Bolzano.

The indicator refers to 2022 and is drawn up on the basis of Istat data relating to the last “Nable Review for Civil Use” carried out in 2023 and published in 2024. The information is provided on a national, regional and by hydrographic district, divided in turn into removal from the surface and underground body water. The levy values are compared with those detected in the previous "Nail census for civil use" of 2020. Also in 2022, compared to the previous 2020 census, the water withdrawal for civil use in Italy has decreased slightly.

The indicator provides a representation of the trend of the average monthly temperatures recorded in the provincial capital city / region during 2021, compared with that of the average monthly temperatures calculated for the same locations over the thirty-year period 1961-1990. During 2021 there was a general increase in average monthly temperatures compared to the reference period, with exceedances of the reference values on average for 8 months and in particular in the summer and winter months. It is mainly the cities of the North where the temperature increases assume significant values in species in the months of February and December. It should be noted that in the months of April and October the temperature values, in most of the capitals, were on average lower than in the reference period.

The indicator provides a measure of coastal engineering interventions that directly alter geomorphology, coastal dynamics and often the natural character of long stretches of coast. The reference data for the calculation of the indicator concern three main aggregations within which the various types of works can be grouped: the port infrastructures, the coastal defense works built near the shore and the set of the other differently characterized structures, which however retain the peculiarity of being leaning against the coastline. The elaborations led to the creation of graphs useful to assess the situation in 2020 of the national coastal artificialization and the variation that took place with reference to the years 2000, 2006 and 2020. In general terms, there is an increase in artificialization ranging from 696 km in 2000, to 714 km in 2006, to 770 km in 2020 (about 8,300 km of national coast), mainly due to the growth of port works and coastal defense works grazing on the coast.

Coastal marine waters are “surface waters located inside an imaginary line, every point of which is one nautical mile seaward from the nearest point of the baseline used to determine the limit of territorial waters, and which may extend up to the outer limit of transitional waters” (Paragraph 1 of Article 74 of Legislative Decree 152/2006). The legislation (Legislative Decree 152/2006) mandates the achievement of a “good” status of water bodies (chemical + ecological) by the dates set by current legislation; failure to achieve environmental objectives results in the implementation of remediation measures. Based on the analysis of data reported by the Districts in the 3rd Reporting to the European Commission for the 2016–2021 six-year period (3rd RBMP), the chemical status of Italian coastal marine waters appears heterogeneous. This heterogeneity is evident both in terms of the number of water bodies identified per district and their classification. The Eastern Alps and Po River Districts have all water bodies in a “not good” chemical status, while in Sicily and the Southern Apennines District, over 60% of the water bodies are in a “not good” status. The Northern Apennines, Central Apennines, and Sardinia Districts, instead, register more than 50%, more than 90%, and more than 80%, respectively, in a “good” chemical status. At the national level, 51% of coastal marine water bodies are in good chemical status. Comparing the 2nd and 3rd RBMPs, in the 2nd RBMP, water bodies with unknown chemical status amounted to 26% (147 out of 561), whereas in the 3rd RBMP, only one water body has an unknown status. Generally, water bodies in good chemical status are comparable between the two RBMPs—52% and 51%, respectively—while water bodies in not good chemical status increased in the 3rd RBMP (49%).

The Chemical Status of Groundwater (SCAS) indicator assesses the chemical quality of Italian groundwater bodies by comparing pollutant concentrations with the Environmental Quality Standards and Threshold Values specified in Tables 2 and 3 of Ministerial Decree (DM) 6/7/2016.

Depending on whether these concentration limits are met, a groundwater body is classified as having either good or poor chemical status. This classification, along with quantitative status, determines the overall groundwater condition. The indicator is based on data from the classification of water bodies reported in WISE Reporting for the 3rd River Basin Management Plan (RBMP).

At the national level, during the 2016-2021 classification period related to the 3rd RBMP, there was an increase in groundwater bodies classified as having good chemical status, reaching 70% of the total (compared to 58% in the 2nd RBMP). The percentage of water bodies classified as poor was 27%.

At the district level, the percentage of groundwater bodies with good chemical status ranges from 56% in the Sicily District to 85% in the Eastern Alps District. Across all hydrographic districts, the number of water bodies with unknown status has significantly decreased compared to the previous cycle, with all water bodies now classified in the Eastern Alps, Southern Apennines, and Sicily Districts.

The indicator provides an assessment of the chemical quality of Italian surface water bodies. The chemical status is evaluated based on the concentration of chemical substances in the water and biota matrices, specifically those listed in the Priority Substances List (Table 1/A of Legislative Decree 152/2006 and subsequent amendments). These substances are classified as priority, priority hazardous, and other substances.

For each substance in the Priority Substances List, Italian legislation—implementing European Directives—establishes Environmental Quality Standards (EQS) that must be met for a water body to be classified as having good chemical status. The chemical status, together with the ecological status, contributes to the overall “environmental status” evaluation of each water body.

The indicator was developed using classification data from the WISE Reporting of the 3rd River Basin Management Plan (RBMP). At both the national and district levels, an increase in the number of water bodies classified as having good chemical status has been observed for rivers and lakes, along with a decrease in the number of unclassified water bodies, compared to the previous cycle.

The legislation (Legislative Decree 152/2006) mandates achieving good status of water bodies (chemical + ecological) by the deadlines established by the current legislation. The analysis of chemical status shows heterogeneous values among the districts, with 100% of water bodies in good status only for the Central Apennines and 52% for Sardinia. In all other districts, the percentage of water bodies in good status never exceeds 50% and ranges from 3% in the Eastern Alps to 40% in the Northern Apennines.

A comparison between the status in the 2nd Water Management Plan (WMP) cycle and that in the 3rd cycle shows maintenance of good chemical status for 100% of the water bodies in the Central Apennines, an improvement for those in the Northern Apennines (from 30% to 40%), Sardinia (from 12% to 52%), and Sicily (from 11% to 17%), and a worsening for the water bodies in the Eastern Alps District (from 51% to 3%), Po River (from 65% to 23%), and Southern Apennines (from 18% to 11%).

At the national level, the number of water bodies in good status is 56 out of 172 (33%) in the 2nd WMP cycle, while in the 3rd cycle it is 42 out of 146 (29%).

Chemical monitoring of groundwater bodies during the period 2018–2020 revealed that the most critical anthropogenic substances on a national scale for chemical status are nitrates and trichloromethane. Among the various substances of potential natural origin present in groundwater bodies, electrical conductivity—related to the presence of chlorides—stands out as an excellent indicator of groundwater salinization. This salinization can stem from marine origins in coastal aquifers or from deep fossil waters.

Between 2014 and 2020, nitrate concentrations remained stable in 78.8% of the monitoring stations, decreased in 11.8%, and increased in the remaining 9.4%. The regions of Abruzzo and Emilia-Romagna reported the highest percentages of stations with decreasing trends (22.8%), while Lazio recorded the highest percentage of stations with increasing trends (20.6%).

Trichloromethane concentrations were stationary in 72.6% of the stations, showed a decreasing trend in 24.9%, and an increasing trend in only 2.5%. High percentages of stations with decreasing trends were observed in Marche (81.4%) and Piedmont (70.7%).

Electrical conductivity trends were stationary in 78.6% of the stations, decreasing in 4.6%, and increasing in the remaining 16.8%. Emilia-Romagna recorded the highest value for decreasing trends (14.5%), while Lazio had the highest percentage of increasing trends (25%).

In 2017, chemical monitoring of watercourses was conducted by ARPA/APPA at a total of 1,867 monitoring stations across 15 regions and 2 autonomous provinces.

The indicator's representation considered both the Environmental Quality Standards - Annual Average (EQS-AA) and Environmental Quality Standards - Maximum Allowable Concentration (EQS-MAC) for surface waters, as defined in Legislative Decree 172/2015.

At the national level, 87.1% of stations showed no exceedances of EQS-AA, and 98.6% of stations showed no exceedances of EQS-MAC.

The indicator provides the national and regional estimate of the state conservation of Italian coasts in 2020 and of the changes due to erosion or progress suffered since 2006, useful for the assessment of the vulnerability of coastal areas and the risk to which urban centers, infrastructure and socio-economic activities that develop near the coast are exposed. In 2020 there was a significant instability over 1,913 km of coastline, of which 943 km for erosion and 970 km for advance, however, compared to the previous surveys (1950-2000, 2000-2006), there is a slight trend to greater stability and an increase in the stretches of coast in progress.

The ecological classification index of the Biological Quality Element "benthic macroinvertebrates," M-AMBI (Multimetric-AZTI Marine Biotic Index), allows a synecological evaluation of the ecosystem under analysis. It is based on the analysis of the structure of benthic macroinvertebrate communities, considering the ecological value of macrozoobenthic species in soft sediments. Species are divided into five ecological groups (first-order opportunistic, second-order opportunistic, tolerant, sensitive/tolerant, and sensitive) based on their sensitivity to gradients of environmental stress. The index describes the quality status of the Biological Quality Element "benthic macroinvertebrates" in five classes: High, Good, Moderate, Poor, and Bad.

Overall, no critical situations were identified for the period 2017–2022 in the coastal regions where data are available. The analysis indicates that 74% of monitoring stations are in High or Good status, while 1% of stations are in Bad status.

In the assessment of the ecological quality of coastal marine environments within the framework of the European Directive 2000/60/EC (implemented through Legislative Decree 152/2006 and subsequent amendments), reference is made to the Biological Quality Element (BQE) Macroalgae. In Italy, as stipulated by Ministerial Decree 260/2010, this BQE is assessed using the CARLIT index (Cartography of littoral and upper-sublittoral benthic communities, or, in short, CARtography of LITtoral), which contributes to the classification of the ecological status of marine-coastal water bodies. For the period 2019–2021, over 80% of analyzed stations met the quality standard (at least "good").

In the assessment of the ecological quality of coastal marine environments within the framework of the European Directive 2000/60/EC (transposed by Legislative Decree 152/2006 and subsequent amendments), reference is made to the Biological Quality Element (BQE) Angiosperms. This BQE in Italy, as provided for by the Ministry of the Environment Decree 260/2010, is evaluated through the PREI (Posidonia Rapid Easy Index). In this context, in fact, the meadows of Posidonia oceanica (L.) Delile take on considerable importance in assessing the ecological quality of coastal marine environments, given their wide distribution and sensitivity to sources of disturbance of anthropogenic origin. The classification of this BQE is carried out where, for reasons of geographical distribution, the meadow is present, i.e., in the Tyrrhenian regions and in Apulia. The data analyzed show that more than 80% of the meadows are in "good" or "high" status.

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.

To contain erosion and damage caused by storms along the Italian coasts, defense interventions are often carried out aimed at protecting goods and infrastructure and restoring beaches. The indicator “coastal defense works” provides the number, on a national and regional basis, of the different types of “rigid” works of coastal defense (islots, mixed works, brushes, grazing and cliffs) and their variation over time. From 2000 to 2020, if on the one hand it was possible to find an increase in the number of rigid defense works (from about 6,600 to 10,500) indicative of the fragility of coastal environments subjected to increasing anthropogenic pressure; on the other hand, the increasing adoption of submerged or partially emerged defense solutions (from 10% in 2006 to 16% in 2020) shows the trend towards the search for a compromise between the hydraulic efficiency of a lesser impact.