
and primary emissions from certain distribution
providers. Well-to-tank emission factors are provided
by DEFRA.
Waste generated in operations
based on DEFRA,
dependent on material type, treatment type, mate-
rial location and material weight.
Business travel
based primary activity data from
service providers using well-to-wheel flight emissions
from DEFRA.
Employee commuting
using Quantis emission factors
based on the average number of full-time equivalent
employees in the reporting year, with well-to-tank
emission factors from DEFRA.
Downstream transportation and distribution
based
on spend-based emission factors from CEDA on truck
transportation.
End-of-life treatment of sold products
based on esti-
mates for materials used in products, using DEFRA
emission factors for material type, country of distri-
bution, assumed treatment type and weight.
SBTi targets
Scope 1+2 target
GHG emission reduction targets follow SBTi guidelines,
covering all production sites. Emissions from sales
offices are excluded, as they account for less than 5%
of scope 1 and 2 GHG emissions. The achieved reduc-
tion is calculated against a 2022 baseline for scope
1 and 2 emissions from production sites, ensuring
consistency in the scope over the years.
Suppliers with science-based targets
The metric measures scope 3 emissions associated
with suppliers that have SBTi targets. The scope 3
categories included in this metric are purchased
goods and services, capital goods, upstream trans-
portation and distribution, business travel and down-
stream transportation and distribution. The denom-
inator is calculated as the total scope 3 emissions
from those categories. To determine the numerator,
suppliers with validated targets or active commit-
ments are identified through the SBTi dashboard at
the end of the financial year. The Supplier Tracker List
is used to document suppliers with validated targets.
Annual percentage target
The metric “Annual % target / Base year” is calculated
by dividing the SBTi target (i.e, -42% and 80%) by
the number of years between the target year and the
base year (respectively, 8 and 6).
Pollution
SoCs and SVHCs are reported as purchased quan-
tities by all production sites, covering both product
supply and research and development activities,
based on invoices or delivery notes from vendors.
Quantities of SoCs and SVHCs that leave ALK’s facili-
ties are not reported, as the estimate would be equal
to amounts procured.
At each site, comprehensive lists of SoC chemicals
are created by using the internal chemical manage-
ment system. SoC chemicals are labelled with one or
more Hazard-statements (H-statements), according
to the Classification, Labelling and Packaging of
chemicals (CLP Regulation) in EU. For production
sites in the USA, where H-statements are not avail-
able, GHS hazard statements (defined by OSHA) are
translated into H-statements to determine which
chemicals are SoCs or SVHCs.
Water
(incl. significant estimate for irrigation as well as
water reused and recycled)
Water consumption
Water is categorised into water for domestic use
(drinking water, sanitary water, and water for
production) and water for irrigation, which is used for
cultivating source materials. For irrigation, the use of
estimates is considered significant.
Water consumption is reported in m
3
based on meter
readings and/or invoices at individual production
sites. When meter readings or invoices are unavail-
able, estimation-based water consumption is used to
calculate water consumption:
• Water irrigation for leased land at Post Falls (USA)
farmland is estimated by multiplying the leased
area by the water consumption intensity factor (m³/
acre) derived from measured data on company
owned land.
• Water usage at leased facilities in Plainville and
Port Washington (USA) production sites is esti-
mated based on square footage occupied by ALK,
as stated in the leasing contract, relative to the
total square footage of the building.
Water storage
ALK does not store water.
Water consumption in areas of high-water stress
This corresponds to water consumption at ALK’s
Madrid (Spain) production site.
Water reused and recycled
Only one leased site in the USA currently reuses water,
as part of a water reclamation program overseen by
the DEQ (Department of Environmental Quality).
Resource use and circular economy
Waste is reported and categorised between treat-
ment methods at site level, based on invoices
received from waste vendor recipients. Operational
waste was either reused, recycled, incinerated, or
sent to landfill, with no other recovery or disposal
methods used.
Some estimates are used to calculate waste:
• General solid waste at Luther and Plainville (USA)
production sites is estimated based on the pickup
cycles reported by the waste vendor for each
quarter.
• For the leased location at 2 Channel at Port Wash-
ington (USA) production site, general solid waste
is not managed internally. Estimation is therefore
based on the average number of garbage bags
collected per day.
• For some USA production sites and Madrid (Spain)
production site, certain types of waste are esti-
mated based on the number of pickups reported
by the waste vendor. These estimates are either
supported by actual waste weight measurements
collected over a defined period and applied as
fixed standards for the waste type, or, when actual
weights are unavailable, derived using conversion
factors published by governmental authorities.
The actual weights of containers or dumpsters are
measured at local production sites over a defined
period.
By default, waste is reported in accordance with the
waste hierarchy of EU waste polices and legislation,
which is described in the EU waste framework direc-
tive (Directive 2008/98/EC).
For production sites in Europe, when there is a
difference between EU and national legislation,
ALK follows the national legislation. Waste types
are categorised by the respective waste vendor
according to the national legislation.
For production sites in the USA, estimation-based
waste is calculated using conversion factors
published by the US EPA.
Intensity calculations
Net revenue amounts are derived from ALK's total
group turnover of the consolidated financial state-
ments (note 2.1, page 94).
Intensity calculations are reported as unit / annual
revenue in million DKK. GHG intensity is calculated
using total emissions (scope 1, 2 and 3) on loca-
tion-based and market-based methods.
All revenue falls under NACE Section C: Manufac-
turing, Division 21: manufacturing of basic pharma-
ceutical products and pharmaceutical preparations
according to Commission Delegated Regulation (EU)
2022/1288. Manufacturing is a high climate impact
sector.
Management's
review
Sustainability
statement
General
information
Environmental
information
Climate change
Pollution
Water
Biodiversity and
ecosystems
Resource use and
circular economy
EU Taxonomy
Accounting policies
– Environmental
information
Social
information
Governance
information
Appendix
Financial
statements
Annual Report 2025 58Environmental information