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Annex

RATTI SPA BENEFIT COMPANY
U.M. M 3
2022 2021 2020 Δ% 2022 on 2021

Tot. water withdrawal 352,023 306,925 266,578 14.69%
from well counters 349,815 305,387 265,077 14.55%
-of which freshwater (≤1000 mg/l of total 349,815 305,387 N/D 14.55%
dissolved solids)
-of which other types of water (> 1,000 mg/l of 0 0 N/D -
total dissolved solids)
WATER WITHDRAWAL
from aqueduct (bill) 2,208 1,538 1,501 43.56%
-of which freshwater (≤1000 mg/l of total 2,208 1,538 N/D 43.56%
dissolved solids)
- of which other types of water (> 1,000 mg/l of 0 0 N/D -
total dissolved solids)
Tot. water withdrawal over total metres of 0.10871 0.09181 0.09164 18.41%
fabric produced
Tot. water discharges into the sewerage 304,375 261,560 219,595 16.37%
system
- of which freshwater (≤1000 mg/l of total 0 0 N/D -
dissolved solids)
WATER DISCHARGES
- of which other types of water (> 1,000 mg/l of 304,375 261,560 N/D 16.37%
total dissolved solids)
Tot. water discharges over total metres of 0.09399 0.07824 0.07549 20.13%
3
fabric produced (m /m)
The Guanzate site is situated in an area with a water stress < 10% (according to data provided by the Aqueduct Water Risk Atlas). As from 2021, Ratti SpA BC includes the distinction called for by GRI, whereby
water consumption must be broken down into freshwater (≤1,000 mg/l of total dissolved solids) and other types of water (>1,000 mg/l of total dissolved solids). This information was not available before
2020.

GRI 303-5 TOTAL WATER CONSUMPTION AND STORAGE OF WATER IN THE RATTI GROUP AND IN RATTI SPA BC

RATTI GROUP
U.M. M 3
2022 2021 2020 Δ% 2022 on 2021

Tot. water withdrawal 47,648 45,365 46,983 5.03%
WATER CONSUMPTION
Tot. water consumption over total metres of 0.01459 0.01346 0.01597 8.40%
fabric produced (m /m)
3
Change in water storage 0 N/D N/D N/D
Water storage at the beginning of the
WATER STORAGE reporting period 300 N/D N/D N/D
Water storage at the end of the reporting 300 N/D N/D N/D
period
The calculation of water consumption, broken down by source and discharges, only includes the Italian and Romanian sites. This is because in Tunisia water consumption and discharges are associated with
water drawn from a well, but that water is not used in the production cycle. The data for the Group coincides with that for Ratti SpA BC, given that water consumption is only associated with the Guanzate
site. The figure for water consumption, seen as the difference between water drawn and water discharged, is > 0, given that some of the water is introduced into the production cycle and then “consumed”
because of a number of factors: natural evaporation within the processes, evaporation in cooling towers, dispersion in the water environment (e.g. humidification during weaving, irrigation).
Data for water storage was gathered for the first time for the 2022 DNF. The Group is committed to continue its current level of monitoring of this information so it can provide a full overview every year.
There is no water storage system for the Group’s subsidiaries (Creomoda, La Maison des Accessoires and Textrom), while for Ratti SpA BC the data is estimated.

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