Data

Public water in data

A longitudinal analysis of the community-verified observations on the state of public drinking fountains in Italy.

Report generated on September 22, 2026. The analyses are recomputed every 24 hours over the full history of observations.

Abstract

This report analyses 1,913 verified observations covering 1,847 italian public drinking fountains, collected by the community between August 06, 2023 and September 21, 2026. As of publication, 87.5% of the verified italian network delivers drinkable water. The report examines the seasonal variation of water status, its year-over-year evolution, the dynamics of failures and recoveries, the freshness of the observations and the territorial distribution of the coverage.

1The sample

The dataset merges points imported from OpenStreetMap with community reports. Every analysis on water status considers verified observations only: photo-backed reports approved one by one by the moderators. The study perimeter is Italy; international coverage gets its own closing section.

46,413mapped fountains
1,913verified observations
1,847observed fountains
562contributing devices
764covered municipalities
4years of observation

Origin of the mapped points: 45,296 from OpenStreetMap, 1,117 added directly by the community.

Fig. 1 Water status across the verified network as of the publication date of this report.

2Methodology

  1. Collection: app users report the state of a fountain with a photo. Each report records water status, position and date.
  2. Verification: every report goes through manual moderation. Only confirmed reports become observations and enter the analyses; rejected and pending ones are excluded.
  3. Unit of analysis: the verified observation, classified into three states — drinkable water, no water, non-drinkable water.
  4. Seasons: the meteorological convention is used (winter = December-February, spring = March-May, summer = June-August, autumn = September-November).
  5. Geographic perimeter: the analyses cover fountains geolocated in Italy only. Points abroad are summarised in a dedicated section, with no detailed analysis.

3Seasonality of water status

Observations from all years are aggregated by meteorological season. The percentage composition by status reveals whether fountain reliability follows the seasonal cycle, for instance winter anti-freeze shutdowns or summer water crises.

Fig. 2 Percentage composition of the observations by meteorological season, all years aggregated.

In the sample, the share of “no water” observations peaks in Winter (33.0% of the seasonal observations).

Tab. 1 Observations by season and water status, absolute values and percentage shares.
Season DrinkableNo waterNot drinkable Total
Winter 61 30 0 91
Spring 243 37 4 284
Summer 1,033 126 11 1,170
Autumn 334 27 7 368

The same signal, read month by month with all years pooled, pinpoints the peaks the four seasonal blocks smooth out. Months without observations are left blank.

Fig. 3 Share of “no water” and “not drinkable” observations by calendar month, all years pooled.

4Year-over-year evolution

The same composition, read year by year, tracks the trajectory of the network over time. Variations reflect both the real state of the fountains and the growth of the community: recent years rest on a much broader base of observations.

Fig. 4 Percentage composition of the observations by calendar year.
Tab. 2 Observations by year and water status, absolute values and percentage shares.
Year DrinkableNo waterNot drinkable Total
2023 17 1 1 19
2024 65 4 2 71
2025 490 72 3 565
2026 1,099 143 16 1,258

5Status dynamics over time

For fountains with at least two verified observations, consecutive observation pairs are analysed (66 pairs in the sample). The transition matrix estimates the probability that a fountain found in one state is found in the same state, or a different one, at the next observation.

75.9% Persistence drinkable fountains found drinkable again
24.1% Degradation drinkable fountains found broken
50.0% Recovery broken fountains found drinkable again
Tab. 3 Transition matrix between consecutive observations of the same fountain: rows = previous state, columns = next state, row-wise percentage shares.
from ↓ / to → DrinkableNo waterNot drinkable
Drinkable 75.9% 24.1% 0.0%
No water 50.0% 50.0% 0.0%
Not drinkable 0.0% 0.0% 0.0%

Reconfirmation decays with time: among fountains found drinkable, the curve shows the share found drinkable again at the next visit, as a function of the interval between the two observations.

Fig. 5 Share of fountains found drinkable again at the next observation, by interval between the two observations; n = observation pairs in the interval. Intervals with no pairs are left blank.

In the observed recoveries, a median of 145 days passes between a failure observation and the first drinkable one. The value also reflects how often the community revisits, not just repair times: read it as an upper bound.

6Freshness of the observations

For every observed fountain we measure the age of its last verified observation. The distribution quantifies how recent the published data is: an observation describes the fountain at the time of the visit, and ages with it.

Fig. 6 Distribution of the observed fountains by age of their last verified observation.

Median age of the last observation: 98 days. 3.7% of the observed fountains have not received a verified observation in over two years: this is where new reports are most valuable.

7Community activity

The monthly series of verified observations measures the pace of data collection. Downstream, the moderation funnel documents the verification process across all received reports, fountains and public toilets included.

Fig. 7 Verified observations per month, full observation window. The dashed line is the 3-month moving average.
JanFebMarAprMayJunJulAugSepOctNovDec
2023 0 0 0 0 0 0 0 17 1 0 1 0
2024 2 1 1 1 1 1 14 33 5 6 4 2
2025 2 1 3 28 18 39 80 191 105 46 23 29
2026 31 23 25 118 89 115 268 412 177 0 0 0
Fig. 8 Monthly intensity of the verified observations by year and calendar month; darker cells mean more observations.
2,266reports received
2,255confirmed
10rejected
1pending

Confirmation rate over decided reports: 99.6%.

8Territorial distribution

Grouping the regions into the three ISTAT macro areas (South and Islands merged) makes the territorial comparison readable at a glance. The composition is computed on the verified network of each area.

Fig. 9 Percentage composition of the verified network by macro area; next to each name, the fountains mapped in the area.

Italian regions ranked by mapped fountains. The drinkable share is computed on fountains with a verified status only, so regions with few verifications express less stable estimates.

Tab. 4 Top regions by mapped fountains, with the drinkable share of their verified network.
Region Fountains Verified Drinkable share
Veneto 227 227
92.5%
Lombardy 225 225
87.6%
Apulia 180 180
76.7%
Lazio 170 170
92.4%
Trentino-South Tyrol 147 147
91.8%
Emilia-Romagna 146 146
87.7%
Liguria 136 136
93.4%
Friuli-Venezia Giulia 112 112
81.3%
Tuscany 102 102
92.2%
Piedmont 99 99
87.9%

The coverage is concentrated: the top 10 municipalities hold 19.1% of the mapped italian fountains, with a median of 1 fountains per municipality. The Gini index of the distribution is 0.502 (0 = evenly spread, 1 = maximum concentration).

9The rest of the world

Outside Italy the coverage is thinner and verifications are few: the numbers below describe the extent of the map, without the detailed analyses reserved for the italian perimeter.

41,458fountains abroad
69covered countries
309verified observations
83.3%drinkable share

Countries with the most mapped fountains: Spain (11,506), France (8,060), Switzerland (4,716), Austria (2,448), Germany (1,989), Hungary (1,663).

10Community ratings

Beyond water status, observations may include a 1 to 5 rating. The distribution of verified ratings measures the perceived quality of the fountains.

Fig. 10 Distribution of the ratings within verified observations that include one.

Average rating: 4.31 out of 5, computed over 338 verified ratings.

11Limitations

  • The sample is not random; observed fountains are the ones users visit, with a likely over-representation of urban and touristic areas.
  • Observation density grows with the community; year-over-year comparisons also reflect this growth, not only the state of the network.
  • The recorded status is the one at visit time; between two observations the real status may change several times without leaving a trace.
  • Moderator verification assesses the credibility of the report; it does not certify chemical analyses of the water.

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