Preisentwicklung auf dem
Arzneimittelmarkt bis
Februar 2026
GKV-Arzneimittelindex
Impressum
Die vorliegende Publikation ist ein Beitrag des
Wissenschaftlichen Instituts der AOK (WldO).
Preisentwicklung auf dem Arzneimittelmarkt
bis Februar 2026
Berlin, März 2026
Salka Enners, Prof. Dr. Michael Thiede
Wissenschaftliches Institut der AOK (WIdO)
im AOK-Bundesverband eGbR – Arbeitsgemeinschaft
von Körperschaften des öffentlichen Rechts
Rosenthaler Str. 31, 10178 Berlin
Geschäftsführender Vorstand:
Dr. Carola Reimann (Vorsitzende)
Jens Martin Hoyer (stellv. Vorsitzender)
http://www.aok-bv.de/impressum/index.html
Registergericht Berlin (Charlottenburg), GsR 634 B
Aufsichtsbehörde:
Senatsverwaltung für Gesundheit, Pflege
und Gleichstellung –SenGPG–
Oranienstraße 106, 10969 Berlin
Satz: Anja Füssel
Titelfoto: KomPart
Nachdruck, Wiedergabe, Vervielfältigung und Verbreitung
(gleich welcher Art), auch von Teilen des Werkes,
bedürfen der ausdrücklichen Genehmigung.
E-Mail: wido@wido.bv.aok.de
Internet: http://www.wido.de
http://www.aok-bv.de/impressum/index.html
http://www.wido.de/
Inhalt
Einleitende Hinweise ............................................................................................................. 4
Teil I: Preisindex im Arzneimittelmarkt.................................................................................. 5
Gesamtmarkt ............................................................................................................................... 5
Festbetrags- und Nicht-Festbetragsmarkt ................................................................................... 8
Preisentwicklung nach Arzneimittelgruppen ............................................................................. 11
Teil 2: Kennwerte der Preisveränderung im Arzneimittelmarkt ........................................... 13
Einzelne Marktsegmente ........................................................................................................... 14
Vergleich der Marktsegmente ................................................................................................... 18
Arzneimittelgruppen .................................................................................................................. 20
Allgemeine methodische Hinweise ...................................................................................... 21
Datenbasis ................................................................................................................................. 22
4 GKV-Arzneimittelindex – Preisinfo 2/2026
Einleitende Hinweise
Die vorliegende Publikation stellt die Preisentwicklung im Fertigarzneimittelmarkt mit
zwei möglichen Berechnungsansätzen dar. Damit wird ermöglicht, dass bei der Dar-
stellung der aktuellen Preisentwicklung einerseits die Verordnungsmengen eines fes-
ten Warenkorbs und andererseits aktuelle Marktbewegungen auf Produktebene stärker
fokussiert werden.
In Teil 1 wird der Preisindex eines definierten Warenkorbs nachgezeichnet. Dabei wer-
den die Preise aller Arzneimittel entsprechend ihrer Verordnungshäufigkeit im Vorjahr
bis zum aktuellen Monat verglichen. Damit ein Arzneimittel hier berücksichtigt wird,
muss es also sowohl im Vorjahr (Basiszeitraum) als auch aktuell (Betrachtungszeit-
raum) auf dem Markt verfügbar gewesen sein. Dabei wird der Effekt umso stärker ge-
wichtet, je häufiger es verordnet wurde. Aktuelle Marktentwicklungen werden damit
auf Preisebene, nicht aber auf Produktebene nachvollzogen.
In Teil 2 werden die Preise aller aktuell verordnungsfähigen Arzneimittel als ungewich-
tete Mittelwerte der Marktsituation der Vormonate gegenübergestellt. Aktuelle Markt-
entwicklungen werden sowohl auf Preisebene als auch auf Produktebene (einschließ-
lich der aktuellen Markteintritte und Marktaustritte und deren individuelle Preise)
nachvollzogen. Dies geschieht unabhängig von der Verordnungshäufigkeit in einem
definierten Zeitraum. Die Analysen basieren auf allem verkehrsfähigen, rezeptpflichti-
gen Arzneimittel, für die eine Preisangabe vorliegt. Diese Arzneimittel können sowohl
von ambulant tätigen Kassenärzten verordnet werden wie auch im Krankenhaus ein-
gesetzt werden.
GKV-Arzneimittelindex – Preisinfo 2/2026 5
Teil I: Preisindex im Arzneimittelmarkt
Gesamtmarkt
Im Folgenden wird der Preisindex im gesamten Arzneimittelmarkt dargestellt.
In Abbildung 1 wird die Preisentwicklung gegenüber Januar 2024 als Preisindex darge-
stellt. Der Preisindex berechnet sich auf der Grundlage der monatlichen Steigerungen.
In Abbildung 2 wird der prozentuale Anstieg zwischen zwei aufeinanderfolgenden Mo-
naten dargestellt.
Mit der Aktualisierung des Warenkorbes können die Werte von vorangegangenen Pub-
likationen abweichen.
Die Tabelle 1 beinhaltet neben den Preisindizes die Änderungswerte gegenüber dem
Vormonat (vgl. Abbildung 1) und dem Monat des Vorjahres.
Abbildung 1: Preisindex im Gesamtmarkt für Fertigarzneimittel
Quelle: GKV-Arzneimittelindex im WIdO 2026
90
91
92
93
94
95
96
97
98
99
100
101
1 2 3 4 5 6 7 8 9 10 11 12 1 2 3 4 5 6 7 8 9 10 11 12 1 2
2024 2025 2026
Preisindex (Jan 2024= 100)
Gesamtmarkt
6 GKV-Arzneimittelindex – Preisinfo 2/2026
Abbildung 2: Preisentwicklung im Gesamtmarkt gegenüber Vormonat in Prozent
Quelle: GKV-Arzneimittelindex im WIdO 2026
-3,0
-2,5
-2,0
-1,5
-1,0
-0,5
0,0
0,5
1,0
1,5
2,0
2,5
3,0
1 2 3 4 5 6 7 8 9 10 11 12 1 2 3 4 5 6 7 8 9 10 11 12 1 2
2024 2025 2026
GKV-Arzneimittelindex – Preisinfo 2/2026 7
Tabelle 1: Ausgewählte Indikatoren der Preisentwicklung von Januar 2025 bis Februar 2026
für Fertigarzneimittel
Jahr Monat
Preisindex Preisanstieg gegenüber
Januar 2024 = 100 Vorjahr in % Vormonat in %
2025 Januar 98,9 -1,1 0,0
Februar 98,8 -1,3 -0,1
März 98,7 -1,4 -0,1
April 98,7 -1,2 0,0
Mai 98,7 -0,8 0,0
Juni 98,6 -0,7 -0,1
Juli 98,8 -0,8 0,2
August 98,8 -0,8 0,0
September 98,7 -0,7 0,0
Oktober 98,7 -0,5 0,0
November 98,6 -0,4 -0,1
Dezember 98,5 -0,5 -0,1
Jahresdurchschnitt 98,7 -0,8 0,0
2026 Januar 98,4 -0,5 -0,1
Februar 98,4 -0,4 0,0
Jahresdurchschnitt 98,4 -0,4 0,0
Quelle: GKV-Arzneimittelindex im WIdO 2026
8 GKV-Arzneimittelindex – Preisinfo 2/2026
Festbetrags- und Nicht-Festbetragsmarkt
Im Folgenden werden die oben beschriebenen Analysen für den Markt der Festbetrags-
arzneimittel vorgestellt. Stichtag zur Abgrenzung beider Marktsegmente ist der jewei-
lige 1. des Analysemonats. Durch Änderungen der Festbetragsfestlegungen kann die
Warenkorbabgrenzung von der in vorangegangenen Publikationen abweichen. Die
Monatswerte werden auf der Grundlage der aktuell gültigen Festbetragsgruppen auch
rückwirkend neu berechnet.
In Abbildung 3 ist die monatliche Preisentwicklung nach den Marktsegmenten Festbe-
tragsmarkt, Nicht-Festbetragsmarkt und Gesamtmarkt als Preisindex dargestellt.
Die Tabelle 2 beschreibt die Indexwerte nach den Marktsegmenten Festbetragsmarkt,
Nicht-Festbetragsmarkt und Gesamtmarkt.
Die monatliche Preisentwicklung im Vergleich zum Vorjahresmonat für die Marktseg-
mente sind in der Tabelle 3 aufgeführt.
Abbildung 3: Preisindex für Fertigarzneimittel nach Marktsegmenten (entsprechend § 35
SGB V)
Quelle: GKV-Arzneimittelindex im WIdO 2026
92
93
94
95
96
97
98
99
100
101
102
1 2 3 4 5 6 7 8 9 10 11 12 1 2 3 4 5 6 7 8 9 10 11 12 1 2
2024 2025 2026
Preisindex (Jan. 2024 = 100) Nicht-Festbetragsmarkt
Festbetragsmarkt
Gesamtmarkt
GKV-Arzneimittelindex – Preisinfo 2/2026 9
Tabelle 2: Preisentwicklung für Fertigarzneimittel nach Marktsegmenten (entsprechend § 35
SGB V) von Januar 2024 bis Februar 2026
Jahr Monat Gesamtmarkt Festbetragsmarkt* Nicht-
Festbetragsmarkt*
2024 Januar 100,0 100,0 100,0
Februar 100,1 100,2 100,1
März 100,1 100,1 100,0
April 99,8 99,6 99,9
Mai 99,5 99,5 99,5
Juni 99,3 99,5 99,2
Juli 99,6 98,2 100,2
August 99,6 98,1 100,3
September 99,4 98,1 100,0
Oktober 99,2 97,6 99,9
November 99,0 97,6 99,6
Dezember 98,9 97,6 99,6
Jahresdurchschnitt 99,5 98,8 99,9
2025 Januar 98,9 97,6 99,5
Februar 98,8 97,6 99,4
März 98,7 97,5 99,3
April 98,7 97,1 99,4
Mai 98,7 97,0 99,5
Juni 98,6 97,0 99,4
Juli 98,8 96,9 99,7
August 98,8 96,9 99,6
September 98,7 96,9 99,6
Oktober 98,7 96,8 99,5
November 98,6 96,7 99,5
Dezember 98,5 96,8 99,3
Jahresdurchschnitt 98,7 97,1 99,5
2026 Januar 98,4 96,7 99,2
Februar 98,4 96,7 99,2
Jahresdurchschnitt 98,4 96,7 99,2
* Die Veränderungswerte sind dann nicht unmittelbar mit den Angaben der Vorperioden vergleichbar, wenn
neue Festbetragsfestlegungen gelten. In den Teilmärkten werden die jeweils aktuellen Marktanteile zu-
grunde gelegt, d. h. die Veränderungswerte basieren damit auf den jeweils aktuellen Marktverhältnissen
und werden rückwirkend neu berechnet Quelle: GKV-Arzneimittelindex im WIdO 2026
10 GKV-Arzneimittelindex – Preisinfo 2/2026
Tabelle 3: Preisentwicklung für Fertigarzneimittel nach Marktsegmenten (entsprechend § 35
SGB V) im Vergleich zum Vorjahr in Prozent
Jahr Monat Gesamtmarkt
in %
Festbetragsmarkt*
in %
Nicht-Festbetrags-
markt* in %
2025 Januar -1,1 -2,4 -0,5
Februar -1,3 -2,6 -0,7
März -1,4 -2,6 -0,8
April -1,2 -2,5 -0,5
Mai -0,8 -2,6 0,0
Juni -0,7 -2,5 0,2
Juli -0,8 -1,2 -0,6
August -0,8 -1,2 -0,7
September -0,7 -1,2 -0,4
Oktober -0,5 -0,8 -0,4
November -0,4 -0,9 -0,1
Dezember -0,5 -0,9 -0,3
Jahresdurchschnitt -0,8 -1,8 -0,4
2026 Januar -0,5 -0,9 -0,3
Februar -0,4 -0,9 -0,1
Jahresdurchschnitt -0,4 -0,9 -0,2
* Die Veränderungswerte sind dann nicht unmittelbar mit den Angaben der Vorperioden vergleichbar, wenn
neue Festbetragsfestlegungen gelten. In den Teilmärkten werden die jeweils aktuellen Marktanteile zu-
grunde gelegt, d. h. die Veränderungswerte basieren damit auf den jeweils aktuellen Marktverhältnissen
und werden rückwirkend neu berechnet
Quelle: GKV-Arzneimittelindex im WIdO 2026
GKV-Arzneimittelindex – Preisinfo 2/2026 11
Preisentwicklung nach Arzneimittelgruppen
In Abbildung 4 ist die Preisentwicklung der Arzneimittelgruppen entsprechend dem ak-
tuellen Stand der ATC-Klassifikation des GKV-Arzneimittelindex im Vergleich zum
Vorjahresmonat dargestellt. Hierbei werden die 20 umsatzstärksten Arzneimittelgrup-
pen berücksichtigt. Tabelle 4 zeigt die Preisentwicklung gegenüber dem Vorjahresmo-
nat, den Umsatzanteil im Gesamtmarkt des Jahres 2024 und die Preisentwicklung ent-
sprechend der aktuellen Festbetragseinstufung in den Arzneimittelgruppen.
Abbildung 4: Preisentwicklung Februar 2026 im Vergleich zum Vorjahresmonat in % nach Arz-
neimittelgruppen
Quelle: GKV-Arzneimittelindex im WIdO 2026
-0,4
-11,5
-4,7
-3,0
-1,7
-1,5
-1,4
-1,4
-1,1
-0,8
-0,7
-0,5
-0,1
-0,1
0,0
0,1
0,6
0,6
0,8
2,1
2,6
-14 -13 -12 -11 -10 -9 -8 -7 -6 -5 -4 -3 -2 -1 0 1 2 3 4
Gesamtmarkt
Andere Mittel für das Nervensystem
Endokrine Therapie
Antivirale Mittel zur systemischen Anwendung
Antineoplastische Mittel
Analgetika
Immunsuppressiva
Antibiotika zur systemischen Anwendung
Psycholeptika
Mittel, die den Lipidstoffwechsel beeinflussen
Mittel mit Wirkung auf das Renin-Angiotensin-System
Andere Dermatika
Psychoanaleptika
Antithrombotische Mittel
Andere Mittel f. d. alimentäre System und d. Stoffwechsel
Ophthalmika
Immunstimulanzien
Antihämorrhagika
Immunsera und Immunglobuline
Mittel bei obstruktiven Atemwegserkrankungen
Antidiabetika
12 GKV-Arzneimittelindex – Preisinfo 2/2026
Tabelle 4: Preisentwicklung in % nach Arzneimittelgruppen für Februar 2026 im Vergleich
zum Vorjahresmonat
ATC
Code
Arzneimittelgruppe nach
2. Ebene der ATC-Klassifikation
Umsatzanteil
im Jahr 2024
in %
Gesamt-
markt
Festbetrags-
markt*
Nicht-Festbe-
tragsmarkt*
A10 Antidiabetika 8,4 2,6 -0,3 3,0
R03 Mittel bei obstruktiven Atemweg-
serkrankungen
4,6 2,1 2,3 2,1
J06 Immunsera und Immunglobuline 1,6 0,8 - 0,8
B02 Antihämorrhagika 2,0 0,6 0,0 1,0
L03 Immunstimulanzien 1,5 0,6 -2,5 1,2
S01 Ophthalmika 3,3 0,1 -0,2 0,2
B01 Antithrombotische Mittel 1,8 0,0 -2,2 0,1
A16 Andere Mittel für das alimentäre
System und den Stoffwechsel
6,7 -0,1 -0,2 0,0
D11 Andere Dermatika 1,9 -0,1 -0,1 -0,4
N06 Psychoanaleptika 1,7 -0,5 - -0,5
C09 Mittel mit Wirkung auf das Renin-
Angiotensin-System
3,8 -0,7 -0,6 -0,9
C10 Mittel, die den Lipidstoffwechsel
beeinflussen
2,1 -0,8 -0,8 -0,8
N05 Psycholeptika 1,7 -1,1 -0,1 -2,4
J01 Antibiotika zur systemischen An-
wendung
1,4 -1,4 -2,6 1,7
L04 Immunsuppressiva 16,5 -1,4 -1,2 -1,5
N02 Analgetika 3,9 -1,5 -1,4 -2,0
L01 Antineoplastische Mittel 7,7 -1,7 -2,1 -1,7
J05 Antivirale Mittel zur systemischen
Anwendung
2,3 -3,0 -3,0 -3,0
L02 Endokrine Therapie 3,1 -4,7 -37,4 -0,3
N07 Andere Mittel für das Nervensys-
tem
1,4 -11,5 -1,6 -12,6
Alle 20 Arzneimittelgruppen 77,1 -0,7 -1,3 -0,5
Gesamtmarkt 100,0 -0,4 -0,9 -0,1
* Die Veränderungswerte sind dann nicht unmittelbar mit den Angaben der Vorperioden vergleichbar, wenn
neue Festbetragsfestlegungen gelten. In den Teilmärkten werden die jeweils aktuellen Marktanteile zu-
grunde gelegt, d. h. die Veränderungswerte basieren damit auf den jeweils aktuellen Marktverhältnissen
und werden rückwirkend neu berechnet
Quelle: GKV-Arzneimittelindex im WIdO 2026
GKV-Arzneimittelindex – Preisinfo 2/2026 13
Teil 2: Kennwerte der Preisveränderung im
Arzneimittelmarkt
Im Folgenden wird die Preisveränderung für den Gesamtmarkt, den Markt der patent-
geschützten Arzneimittel und für neu eingeführte, patentgeschützte Arzneimittel für
den Zeitraum der letzten 24 Monate inklusive des aktuellen Analysemonats dargestellt.
Die Analysen basieren auf den Apothekenverkaufspreisen (AVP). Ist für ein Arzneimit-
tel kein AVP gemeldet, wird ersatzweise der Apothekeneinkaufspreis oder der Herstel-
lerabgabepreis genutzt. Berücksichtigt werden jeweils alle verkehrsfähigen, rezept-
pflichtigen Arzneimittel, für die eine Preisangabe vorliegt.
In Abbildung 5 sind die monatlichen arithmetischen Mittelwerte und die Mediane für
den Gesamtmarkt angegeben. In Tabelle 5 werden die zehn teuersten Arzneimittel des
aktuellen Monats mit ihren Preisen aufgelistet.
Abbildung 5: Preisveränderung im gesamten Arzneimittelmarkt
Quelle: GKV-Arzneimittelindex im WIdO 2026
0
500
1000
1500
2000
2500
3 4 5 6 7 8 9 10 11 12 1 2 3 4 5 6 7 8 9 10 11 12 1 2
2024 2025 2026
D
ur
ch
sc
hn
itt
sp
re
is
in
E
ur
o
Arithmetisches Mittel
Median
14 GKV-Arzneimittelindex – Preisinfo 2/2026
Tabelle 5: Die zehn teuersten Arzneimittel* im Februar 2026
Rang Handelsname ATC
Code
Arzneimittelgruppe nach
2. Ebene der ATC-Klassi-
fikation
Hauptindikationsgruppe Preis
(in Euro)
1 Upstaza A16 Enzymersatzmittel Seltene Stoffwechselkrank-
heiten
3.000.000
2 Hemgenix B02 Antihämorrhagika Erkrankungen des Blutsys-
tems
2.482.100
3 Libmeldy A16 Enzymersatzmittel Seltene Stoffwechselkrank-
heiten
2.125.000
4 Zolgensma M09 Antiarthrotika/andere
Mittel
Erkrankungen des Muskel-
und Skelettsystems
1.385.000
5 Carvykti L01 Antineoplastische Mittel Krebserkrankungen 285.000
6 Luxturna S01 Ophthalmika Erkrankungen von Auge
und Ohr
280.000
7 Tecartus L01 Antineoplastische Mittel Krebserkrankungen 271.000
8 Idefirix L04 Immunsuppressiva Immuntherapie 249.510
9 Kymriah L01 Antineoplastische Mittel Krebserkrankungen 239.000
10 Yescarta L01 Antineoplastische Mittel Krebserkrankungen 226.990
* aufgeführt ist die teuerste, sich in Vertrieb befindende Packung des Arzneimittels
Quelle: GKV-Arzneimittelindex im WIdO 2026
Einzelne Marktsegmente
Tabelle 6 enthält die Durchschnittswerte entsprechend der Abbildung 5 und zusätzlich
die Preisveränderung für die preiswertesten und die teuersten Produkte am Markt. Ta-
belle 7 beschreibt die aktuelle monatliche Preisveränderung im patentgeschützten
Markt, Tabelle 8 für die neu eingeführten Patent-Arzneimittel. Im Warenkorb sind alle
Neueinführungen der zu jedem dargestellten Monat vorangegangenen 36 Monate ent-
halten. Dies entspricht beispielsweise für Februar 2026 dem Warenkorb der Neueinfüh-
rungen zwischen Februar 2023 und Februar 2026. Aufgrund der geringen Anzahl von
Produkten wurde die Anteilsgrenze in Tabelle 8 auf 5 % gesetzt.
GKV-Arzneimittelindex – Preisinfo 2/2026 15
Tabelle 6: Veränderung der durchschnittlichen Preise für verschreibungspflichtige Fertigarz-
neimittel (in Euro)
Jahr Monat
Preis-
werteste
Produkte
(1%)
Preis-
werteste
Produkte
(25%)*
Arithmeti-
sches
Mittel
Teuerste
Produkte
(25%)**
Teuerste
Produkte
(1%)**
2024 März 12,52 18,64 1.806,78 7.057,01 142.672,58
April 12,56 18,64 1.779,23 6.948,50 139.624,53
Mai 12,55 18,66 1.775,85 6.933,53 139.422,17
Juni 12,55 18,66 1.760,44 6.871,39 137.712,93
Juli 12,57 18,66 1.735,77 6.773,79 134.712,65
August 12,56 18,69 1.740,32 6.784,29 134.779,61
September 12,59 18,74 1.743,62 6.799,72 133.137,76
Oktober 12,59 18,75 1.745,97 6.809,00 133.261,34
November 12,59 18,79 1.743,25 6.798,71 131.451,78
Dezember 12,61 18,81 1.743,82 6.794,84 131.475,50
2025 Januar 12,61 18,83 1.738,87 6.774,20 131.398,82
Februar 12,64 18,86 1.732,43 6.752,08 131.852,08
März 12,63 18,89 1.710,13 6.663,07 129.385,69
April 12,63 18,90 1.968,96 7.695,86 153.101,73
Mai 12,67 18,96 1.973,16 7.714,10 155.181,01
Juni 12,68 19,00 1.978,31 7.732,02 155.308,33
Juli 12,74 19,04 1.972,25 7.708,55 155.227,03
August 12,75 19,07 1.943,73 7.595,40 151.933,72
September 12,74 19,09 1.946,61 7.602,87 150.440,43
Oktober 12,76 19,13 1.948,04 7.609,35 150.229,76
November 12,75 19,16 1.951,40 7.619,84 150.642,80
Dezember 12,77 19,19 1.956,69 7.640,52 150.910,28
2026 Januar 12,77 19,19 1.980,46 7.733,57 153.071,90
Februar 12,77 19,19 1.977,69 7.724,05 152.940,01
* ungewichtete Durchschnittspreise der preiswertesten Arzneimittel entsprechend dem angegebenen Anteil
** ungewichtete Durchschnittspreise der teuersten Arzneimittel entsprechend dem angegebenen Anteil
Quelle: GKV-Arzneimittelindex im WIdO 2026
16 GKV-Arzneimittelindex – Preisinfo 2/2026
Tabelle 7: Veränderung der durchschnittlichen Preise für patentgeschützte verschreibungs-
pflichtige Fertigarzneimittel (in Euro)
Jahr
Monat
Preis-
werteste
Produkte
(1%)
Preis-
werteste
Produkte
(25%)*
Arithmeti-
sches
Mittel
Teuerste
Produkte
(25%)**
Teuerste
Produkte
(1%)**
2024 März 20,35 140,68 22.697,82 86.291,46 1.380.000,00
April 20,28 138,23 22.257,43 84.557,67 1.338.333,33
Mai 20,28 140,57 22.075,17 83.854,84 1.338.333,33
Juni 20,28 142,72 21.704,25 82.346,75 1.315.833,33
Juli 20,47 145,99 21.226,10 80.120,81 1.266.166,67
August 20,54 150,54 21.109,57 79.616,09 1.266.166,67
September 20,54 147,70 20.917,27 79.025,50 1.266.166,67
Oktober 20,54 148,25 20.755,74 78.221,13 1.266.166,67
November 20,54 149,91 20.588,71 77.560,05 1.266.166,67
Dezember 20,54 149,84 20.584,12 77.559,27 1.266.166,67
2025 Januar 20,54 162,13 21.183,45 79.660,06 1.266.166,67
Februar 20,54 162,11 21.010,55 78.983,93 1.266.000,00
März 20,54 161,01 20.549,36 77.580,01 1.266.000,00
April 20,54 167,73 24.072,24 91.139,56 1.558.333,33
Mai 20,54 170,35 23.931,01 90.802,29 1.558.333,33
Juni 20,54 174,15 23.834,99 90.276,10 1.558.333,33
Juli 20,85 177,50 23.871,29 90.258,93 1.558.333,33
August 20,85 178,67 23.346,74 88.521,78 1.516.666,67
September 20,85 183,59 23.176,66 87.569,79 1.516.666,67
Oktober 20,85 186,16 23.030,86 86.954,05 1.516.666,67
November 20,85 185,71 22.951,03 86.746,31 1.516.666,67
Dezember 20,85 182,86 22.497,58 84.891,43 1.516.666,67
2026 Januar 20,85 170,66 22.594,21 85.688,54 1.554.758,35
Februar 21,67 169,93 22.544,97 85.086,76 1.371.364,30
* ungewichtete Durchschnittspreise der preiswertesten Arzneimittel entsprechend dem angegebenen Anteil
** ungewichtete Durchschnittspreise der teuersten Arzneimittel entsprechend dem angegebenen Anteil
Durch monatliche Patentausläufe und damit verbundene Klassifikationsänderungen kann die Marktabgrenzung
zwischen patentgeschütztem Markt und generikafähigem Markt von Monat zu Monat differieren. Die Zuschrei-
bung zu einem der Marktsegmente erfolgt einheitlich auch rückwirkend. Ein Vergleich der vorgestellten Analysen
mit vorherigen Publikationen ist daher nur bedingt aussagekräftig, da immer die aktuelle Klassifikation zugrunde
gelegt wird.
Quelle: GKV-Arzneimittelindex im WIdO 2026
GKV-Arzneimittelindex – Preisinfo 2/2026 17
Tabelle 8: Veränderung der durchschnittlichen Preise der Marktneueinführungen im Markt
der patentgeschützten verschreibungspflichtigen Fertigarzneimittel (in Euro)
Jahr Monat
Preis-
werteste
Produkte
(5 %)*
Preis-
werteste
Produkte
(25 %)*
Arithmeti-
sches
Mittel
Teuerste
Produkte
(25 %)**
Teuerste
Produkte
(5 %)**
2024 März 46,65 234,59 59.398,20 229.652,33 1.044.733,24
April 41,34 232,09 57.263,49 216.265,47 965.685,57
Mai 40,43 243,18 56.698,96 215.800,28 965.685,57
Juni 41,06 248,70 39.809,24 151.198,40 637.958,89
Juli 46,87 268,35 39.944,52 150.447,36 605.498,07
August 50,85 312,75 39.277,27 145.953,49 605.498,07
September 46,40 283,78 38.041,14 141.731,35 605.498,07
Oktober 47,33 330,46 38.950,56 146.158,75 605.498,07
November 47,12 333,70 37.704,68 141.521,75 602.916,66
Dezember 46,13 355,51 37.957,08 141.521,75 602.916,66
Januar 52,96 389,78 39.062,77 145.325,34 602.023,80
2025 Februar 53,19 371,45 38.183,86 141.997,10 575.725,69
März 53,36 390,01 39.081,49 147.324,13 575.725,69
April 53,36 432,18 53.903,96 206.133,81 857.023,80
Mai 53,51 456,66 53.294,56 200.669,08 857.023,80
Juni 53,51 441,49 52.533,31 200.982,43 857.023,80
Juli 53,51 453,92 53.631,77 200.897,40 857.023,80
August 53,64 447,88 50.661,19 193.187,82 821.309,52
September 62,65 464,23 27.574,79 101.349,76 399.440,02
Oktober 59,24 476,17 25.579,83 93.745,08 371.726,79
November 59,44 506,13 25.822,35 93.840,56 364.890,53
Dezember 64,66 358,59 24.236,14 87.514,87 364.890,53
2026 Januar 86,09 286,28 24.327,56 89.582,66 351.635,70
Februar 91,20 276,39 24.304,77 89.075,25 351.635,70
* ungewichtete Durchschnittspreise der preiswertesten Arzneimittel entsprechend dem angegebenen Anteil
** ungewichtete Durchschnittspreise der teuersten Arzneimittel entsprechend dem angegebenen Anteil
Quelle: GKV-Arzneimittelindex im WIdO 2026
18 GKV-Arzneimittelindex – Preisinfo 2/2026
Vergleich der Marktsegmente
In Abbildung 6 wird die monatliche Veränderung der ungewichteten durchschnittlichen
Preise im Gesamtmarkt, im patentgeschützten Markt und für die Marktneueinführun-
gen dargestellt.
Abbildung 6: Preisveränderung nach Marktsegmenten in Euro
Quelle: GKV-Arzneimittelindex im WIdO 2026
0
10.000
20.000
30.000
40.000
50.000
60.000
70.000
80.000
3 4 5 6 7 8 9 10 11 12 1 2 3 4 5 6 7 8 9 10 11 12 1 2
2024 2025 2026
D
ur
ch
sc
hn
itt
sp
re
is
in
E
ur
o
Patentmarkt
Neue Markteinführungen
Gesamtmarkt
GKV-Arzneimittelindex – Preisinfo 2/2026 19
Abbildung 7 zeigt die Verteilung der Arzneimittelpreise im Gesamtmarkt, im Patent-
markt und im Markt neu eingeführte Arzneimittel im patentgeschützten Markt für den
aktuellen Monat.
Abbildung 7: Preisverteilung nach Marktsegmenten nach Perzentilen
* logarithmische Skalierung zur Basis 10 Quelle: GKV-Arzneimittelindex im WIdO 2026
1
10
100
1.000
10.000
100.000
1.000.000
10.000.000
5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 85 90 95 100
D
ur
ch
sc
hn
itt
sp
re
is
in
E
ur
o*
Neueinführungen Patent Gesamt
(n = 7.988)
(n = 146)
(n = 601)
20 GKV-Arzneimittelindex – Preisinfo 2/2026
Arzneimittelgruppen
Die 20 Arzneimittelgruppen, die die höchste prozentuale Dynamik der Durchschnitts-
preise im Vergleich zum Vorjahresmonat erkennen ließen, werden in Abbildung 8 aus-
gewiesen. Dabei werden die Gruppen entsprechend dem aktuellen Stand der ATC-
Klassifikation des GKV-Arzneimittelindex berücksichtigt, wenn mindestens zehn un-
terschiedliche Präparate am Markt vertreten waren.
Abbildung 8: Änderungen der ungewichteten Durchschnittspreise für Fertigarzneimittel im
Februar 2026 im Vergleich zum Vorjahresmonat in % getrennt nach Arzneimittelgruppen
Quelle: GKV-Arzneimittelindex im WIdO 2026
14,2
-28,6
-21,7
-15,8
-11,2
-11,2
-10,2
-10,0
-9,9
9,9
16,6
18,4
21,6
24,1
27,5
51,5
95,0
141,1
162,5
2.091,3
3.575,2
-500 500 1.500 2.500 3.500
Gesamtmarkt
Gallen- und Lebertherapie
Corticosteroide zur systemischen Anwendung
Endokrine Therapie
Mittel gegen Protozoen-Erkrankungen
Andere Mittel für das Nervensystem
Antineoplastische Mittel
Immunsera und Immunglobuline
Mittel mit Wirkung auf das Renin-Angiotensin-System
Andere Dermatika
Antidiabetika
Aknemittel
Antidiarrhoika und intestinale Antiphlogistika/Antiinfektiva
Rhinologika
Psychoanaleptika
Andere Hämatologika
Gichtmittel
Mittel, die den Lipidstoffwechsel beeinflussen
Herztherapie
Antihämorrhagika
Schilddrüsentherapie
GKV-Arzneimittelindex – Preisinfo 2/2026 21
Allgemeine methodische Hinweise
Die vorliegenden Analysen ermöglichen einen Überblick über die Preisentwicklung im
deutschen Markt der rezeptpflichtigen Arzneimittel. Im Wesentlichen werden dafür
zwei Gruppen von Kennzahlen für verschiedene Marktsegmente ermittelt und monat-
lich zur Verfügung gestellt.
Die Preisindices werden nach der Laspeyres-Formel berechnet. Bei der Indexberech-
nung werden nur solche Artikel berücksichtigt, die im Warenkorb des Basisjahres 2024
enthalten sind. Dabei werden in der vorliegenden Publikation alle Arzneimittel berück-
sichtigt, die sich in der Basis- und Berichtsperiode im Abverkauf befinden. Eventuelle
indirekte Preiserhöhungen im Zusammenhang mit Produktvariationen im Berichtszeit-
raum werden nicht erfasst. Insbesondere werden auch neue Präparate, deren Marktein-
tritt nach der Erhebung des Warenkorbes liegt, nicht berücksichtigt, da noch keine ent-
sprechenden Verordnungsdaten vorliegen.
Neben der Berechnung der Indices werden ergänzend Preisanalysen angeboten. Für die
Berechnung der reinen Preisentwicklung werden alle Präparate – also insbesondere
auch neue Produkte und Produktvariationen – zum Zeitpunkt des Berichtsmonats be-
rücksichtigt. Diese Analysen können ohne Berücksichtigung der Abverkaufszahlen als
Lageparameter für die diskutierten Marktsegmente erstellt werden.
Bei der Interpretation der Ergebnisse ist auf die unterschiedliche Aussagekraft der bei-
den Betrachtungen zu achten. Während der Preisindex als Maß für die Teuerung für
einen definierten Warenkorb interpretiert werden kann, zeigen die Lageparameter, wie
sich die Verteilung der Preise unabhängig von einem Warenkorb in dem Betrachtungs-
zeitraum verändert.
Durch monatliche Klassifikationsänderungen kann die Abgrenzung zwischen einzel-
nen Marktsegmenten von Monat zu Monat differieren. Ein Vergleich der Analysen mit
denen aus vorherigen Publikationen ist daher nur bedingt aussagekräftig, da immer die
aktuelle Klassifikation zugrunde gelegt und die zurückliegenden Zeiträume entspre-
chend neu berechnet werden.
22 GKV-Arzneimittelindex – Preisinfo 2/2026
Datenbasis
Preise
Das GKV-Abrechnungsverzeichnis Arzneimittel enthält Informationen zu über 80.000
Fertigarzneimitteln, die zu Lasten der Gesetzlichen Krankenversicherung abgerechnet
werden können. Preisänderungen werden monatlich berücksichtigt und im GKV-Arz-
neimittelindex historisiert. Stichtag der monatlichen Indexangaben ist der Erste eines
Monats. Jahresdurchschnitte der Preisindices werden als ungewichtete arithmetische
Mittel der Monatswerte errechnet. Die Analysen basieren auf den Apothekenverkaufs-
preisen (AVP).
Die ungewichteten Durchschnittspreise in Teil 2 werden mit den Durchschnittswerten
für ein Arzneimittel mit allen Produktvariationen berechnet. Ist für ein Arzneimittel
kein AVP gemeldet, wird in Teil 2 ersatzweise der Apothekeneinkaufspreis oder der
Herstellerabgabepreis genutzt. In diesen Fällen blieben die Aufschläge der Handelsstu-
fen und die Mehrwertsteuer unberücksichtigt. Anders als in Teil 1 werden in Teil 2 ab
dem Preisinfo 10/2019 auch Klinikpackungen berücksichtigt. Die Analysen basieren so-
mit auf allen verkehrsfähigen befindlichen, rezeptpflichtigen Arzneimitteln mit Preis-
angabe.
Warenkorb
Warenkorbänderungen für die Indexberechnung erfolgen jährlich. Den gegenwärtigen
Warenkorb bilden die gesamten GKV-Arzneimittelverordnungen des Jahres 2024. Mit
der Aktualisierung des Warenkorbes können sich andere Steigerungsraten ergeben, als
sie auf der Basis älterer Warenkörbe ausgewiesen wurden. Diese Differenzen sind je-
doch in aller Regel nur geringfügig.
Umbasierung
Um die aktuellen Indices mit denen älterer Veröffentlichungen zu vergleichen, ist der
aktuelle Index mit der Basis Januar 2024 = 100 auf die damals gültige Basis Januar
2023 = 100 umzurechnen. Der anzuwendende Faktor errechnet sich aus dem Quotien-
ten des Preisindexes des aktuellen Basisjahres (Januar 2024 = 100,1) und der damals gel-
tenden Basis (Januar 2023 = 100).
100,1
= 1,001
100
Eine Umrechnung des Preisindexes für Februar 2026 auf Basis Januar 2023 führt zu ei-
nem Preisindex von 98,4 * 1,001 = 98,5.
Einleitende Hinweise
Teil I: Preisindex im Arzneimittelmarkt
Gesamtmarkt
Festbetrags- und Nicht-Festbetragsmarkt
Preisentwicklung nach Arzneimittelgruppen
Teil 2: Kennwerte der Preisveränderung im Arzneimittelmarkt
Einzelne Marktsegmente
Vergleich der Marktsegmente
Arzneimittelgruppen
Allgemeine methodische Hinweise
Datenbasis
30.03.2026
Datei
PD
DG ENV, Unit B01
March 2026
Packaging and
Packaging Waste
Regulation (PPWR)
Frequently Asked Questions
EUROPEAN COMMISSION
Directorate-General for Environment
Directorate ENV.B — Competitive Circular Economy & Clean Industrial Policy
Unit ENV.B.1 — Bioeconomy & Sustainable Materials
Contact: Unit B.1
E-mail: ENV-B01-ARES@ec.europa.eu
European Commission
B-1049 Brussels
EUROPEAN COMMISSION
Directorate-General for Environment
2026
Packaging and Packaging Waste
Regulation (PPWR)
Frequently Asked Questions
Manuscript completed in March 2026
1st edition
This document has been prepared for the European Commission however it reflects the views only of the
authors, and the European Commission is not liable for any consequence stemming from the reuse of this
publication. It is intended to assist economic operators, national authorities and citizens in the application
of the PPWR.
Luxembourg: Publications Office of the European Union, 2026
© European Union, 2026
The reuse policy of European Commission documents is implemented by Commission Decision
2011/833/EU of 12 December 2011 on the reuse of Commission documents (OJ L 330, 14.12.2011, p. 39).
Unless otherwise noted, the reuse of this document is authorised under a Creative Commons Attribution
4.0 International (CC BY 4.0) licence (https://creativecommons.org/licenses/by/4.0/). This means that
reuse is allowed provided appropriate credit is given and any changes are indicated.
For any use or reproduction of elements that are not owned by the European Union, permission may need
to be sought directly from the respective rightholders.
PDF ISBN 978-92-68-37678-2 doi:10.2779/6056528 KH-01-26-006-EN-N
https://creativecommons.org/licenses/by/4.0/
2
Table of Contents
I. Introduction on the subject matter and scope .................................................................. 5
II. Definitions ............................................................................................................................ 6
III. Substances of concern ....................................................................................................... 10
IV. Recyclability ...................................................................................................................... 15
V. Recycled content in plastic packaging ............................................................................. 19
VI. Compostability .................................................................................................................. 23
VII. Packaging minimisation ................................................................................................... 24
VIII. Labelling ............................................................................................................................ 27
IX. Environmental claims ....................................................................................................... 28
X. Obligations of manufacturers .......................................................................................... 29
XI. Empty space....................................................................................................................... 31
XII. Bans and the use of certain packaging ............................................................................ 32
XIII. Reuse and refill .................................................................................................................. 35
XIV. Plastic carrier bags ........................................................................................................... 40
XV. Assessment of the conformity of packaging .................................................................... 41
XVI. Waste prevention .............................................................................................................. 45
XVII. Extended producer responsibility .................................................................................... 47
XVIII. Return and collection systems .......................................................................................... 49
XIX. Deposit and return systems .............................................................................................. 50
3
Abbreviations
CMO: Regulation (EU) No 1308/2013 of the European Parliament and of the Council of
17 December 2013 establishing a common organisation of the markets in
agricultural products
DfR: Design for recycling
DRS: Deposit and Return System
DSA: Regulation (EU) 2022/2065 of the European Parliament and of the Council of
19 October 2022 on a Single Market for Digital Services
ECHA: European Chemicals Agency
EO: Economic Operator
EPR: Extended Producer Responsibility
EPS: Expanded Polystyrene
ESPR: Regulation (EU) 2024/1781 of the European Parliament and of the Council of 13
June 2024 establishing a framework for the setting of eco-design requirements for
sustainable products
FCM: Food-contact material, as regulated under Regulation (EC) No 1935/2004 of the
European Parliament and of the Council of 27 October 2004 on materials and
articles intended to come into contact with food
FIBC: Flexible Intermediate Bulk Container
HoReCa: Hotel, Restaurant and Catering
IBC: Intermediate bulk containers
JRC: Joint Research Centre
NACE: Statistical classification of economic activities / classification of economic
activities in the European Union (EU)
OJEU: Official Journal of the European Union
PFAS: Per-and polyfluoroalkyl substances
PPWD: European Parliament and Council Directive 94/62/EC of 20 December 1994 on
packaging and packaging waste
PPWR: Regulation (EU) 2025/40 of the European Parliament and of the Council of 19
December 2024 on packaging and packaging waste
PRO: Producer Responsible Organisation
REACH: Regulation (EC) No 1907/2006 of the European Parliament and of the Council of
18 December 2006 concerning the Registration, Evaluation, Authorisation and
Restriction of Chemicals (REACH), establishing a European Chemicals Agency
SoC: Substances of Concern
SUPD: Directive (EU) 2019/904 of the European Parliament and of the Council of 5 June
2019 on the reduction of the impact of certain plastic products on the environment
4
TRIS: Procedure under Directive 2015/1535 to prevent creating barriers in the internal
market
WFD: Directive 2008/98/EC of the European Parliament and of the Council of 19
November 2008 on waste
XPS: Extruded Polystyrene
5
I. INTRODUCTION ON THE SUBJECT MATTER AND SCOPE
Regulation (EU) 2025/40 (1) establishes a harmonised legal framework for packaging and
packaging waste across the European Union. Its primary objective is to ensure the smooth
functioning of the internal market while significantly reducing the environmental and health
impacts associated with packaging throughout its life cycle. By replacing Directive 94/62/EC (2),
this regulation introduces clearer, stricter, and more uniform requirements for all economic
operators and Member States, fostering a transition towards a circular economy.
The scope of the Regulation is comprehensive. It applies to all packaging placed on the EU market,
whether empty or filled, regardless of the material used, and whether produced within the Union
or imported from third countries. It also covers all packaging waste generated within the EU.
Packaging is defined broadly, as any item intended for containment, protection, handling, delivery,
or presentation of products, including its components. However, items that form an integral part of
a product and are disposed of together with it are excluded.
Through these provisions, Regulation (EU) 2025/40 seeks to harmonise national measures on
packaging, prevent market fragmentation, and promote sustainable practices. It introduces
obligations such as recyclability and reuse targets, restrictions on hazardous substances, and
requirements for eco-friendly design and labelling. In doing so, it not only addresses pressing
environmental challenges but also creates a level playing field for businesses operating across
multiple Member States.
The PPWR entered into force on 11 February 2025, and its general application date is 12 August
2026, but certain provisions apply later (e.g., recyclability, recycled content targets, packaging bans
and reuse targets by 2030).
Some of the main provisions of the PPWR are:
- Waste Prevention Targets: 5% by 2030, 10% by 2035, 15% by 2040 (compared to 2018
levels) (Article 43).
- Recyclability: All packaging must be recyclable in an economically viable way by 2030
(Article 6).
- Reuse Targets: For transport, e-commerce, and beverage packaging (Article 29).
- Restrictions: Ban on certain single-use formats from 1 January 2030 (Article 25 and
Annex V); PFAS in food contact packaging prohibited from 12 August 2026 (Article 5(5)).
- Empty Space threshold: Max 50% for grouped, transport, and e-commerce packaging
(Article 24).
- Mandatory Deposit-Return Systems: For beverage cans and plastic bottles (Article 50).
- Labelling: Harmonised sorting labels for all packaging (Article 12(1)).
- Extended Producer Responsibility (EPR): Strengthened obligations for producers
(Articles 44–47).
This document clarifies some issues and answers questions that have been received by DG
Environment since the adoption of the Regulation. This document complements the Commission
Notice - Guidance document for Regulation 2025/40 (EU) on packaging and packaging waste
(hereinafter ‘Commission guidance document’).
(1) Regulation (EU) 2025/40 of the European Parliament and of the Council of 19 December 2024 on
packaging and packaging waste, amending Regulation (EU) 2019/1020 and Directive (EU) 2019/904,
and repealing Directive 94/62/EC (OJ L, 2025/40, 22.1.2025).
(2) European Parliament and Council Directive 94/62/EC of 20 December 1994 on packaging and
packaging waste (OJ L 365 31.12.1994, p. 10).
6
II. DEFINITIONS
1) Does the wording packaging ‘…whether empty or with a product…’ modify the
definitions of packaging and of manufacturer under the PPWR?
Article 3(1), point (1), contains a definition of packaging, which remained largely unchanged
compared to the packaging definition in the Directive 94/62/EC. However, the new definition
contains the new wording ‘…whether empty or with a product…’. This new wording does not
modify the definition of packaging or the definition of manufacturer but is intended to cover all
different factual situations and types of packaging that come within the scope of the PPWR. For
further information on the packaging definition, please consult the Commission guidance
document.
2) Why does the definition of packaging for tea and coffee mention ‘machine use’ only
in point (g) and not in point (f) of Article 3(1)?
The wording indicates the difference between systems for filter coffee/tea bags and those for coffee
extraction machines. Machine use is one of the key criteria to decide if a tea/coffee capsule falls
under Article 3(1), point (1)(f), or point (1)(g). Permeability is another element that needs to be
considered.
This distinction is important in relation to the compostability requirements in Article 9. Permeable
tea, coffee or other beverage bags, or soft after-use system single-serve units that contain tea, coffee
or another beverage, which are intended to be used and disposed of together with the product (point
(1)(f)), are mandatorily compostable. Non-permeable tea, coffee or other beverage system single-
serve units intended for use in a machine, and which are used and disposed of together with the
product (point (1)(g)) are not. However, Member States may decide to make the latter mandatorily
compostable on their territories, under certain conditions, such as the existence of an appropriate
collection and waste treatment infrastructure for bio-waste. Member States cannot ban or require
compostability as regards metal capsules.
3) Why does the wording ‘making available on the market’ sometimes refer to the Union
market and other times to the territory of a Member State?
The definitions ‘making available on the market’ (Article 3(1), point (9)) and ‘placing on the
market’ (Article 3(1), point (10)) refer to the Union market. These definitions apply throughout the
PPWR reflecting the harmonisation of requirements that apply directly to economic operators.
However, in the provisions on waste management, such as waste reduction and recycling targets,
separate collection and extended producer responsibility, the requirements are mainly addressed to
Member States.
To reflect the territorial scope of the above-mentioned requirements, the Regulation uses the term
‘making available on the territory of a Member State’ (Article 3(1), point (11)). The definition has
the same meaning as the definition of ‘making available on the market’, the only difference being
that it circumscribes the actions to the territory of a Member State instead of the Union market.
4) How can producers know if a packaged product is made available to an end user or
whether it is made further available?
A product is considered to have been made available on the market when it is supplied for
distribution, consumption, or use in the course of a commercial activity. An end user, whether a
consumer or a professional end user, is a person or entity to whom a product is made available and
who does not make that product further available on the market in the form in which it was
supplied.
7
The determining factor is therefore not the legal status of the recipient, but how the product is
used. A professional end user is considered as an end user where it uses the product on its own
operations or production process and does not resell or otherwise place the product back on the
market in the same form.
A producer of a packaged product should be able to determine, based on the nature of the packaging
and the chosen marketing and distribution channels, whether the intended recipient is an end user
(consumer or professional), or a commercial buyer who will resell the packaged product in another
Member State.
It should be noted that logistics companies that receive packaged goods, such as imported products
from third countries, and perform handling activities (e.g., unpacking, repacking, or dividing
products into smaller quantities) are not considered end users.
5) Is a farmer producer for the purpose of EPR obligations?
Whether a farmer is a ‘producer’ will depend on the specific situation. There is no general
exemption for specific sectors such as farmers in terms of extended producer responsibility
obligations since all economic operators making packaging available on the territory of a Member
State for the first time will have to comply with these obligations.
The following examples show some typical examples of when a farmer would normally be
considered a producer and when it would not.
• If a farmer packs a few apples in a container (sales packaging) and sells it under its own
name or trademark to a retailer or consumer in the same Member State, the farmer is a
producer.
• If the farmer sells the packed apples under its own name or trademark in another Member
State, the farmer is only the producer if the recipient is the end user of the apples. This
means that the farmer is not the producer if it sells the apples to a retailer in another
Member State.
• If the farmer is a micro-enterprise, which is often the case, and the supplier of the apple
container is established in the same Member State, such supplier becomes the producer in
the Member State where the farmer and supplier are located.
• If the container is produced under the name or trademark of an agricultural cooperative of
which the farmer is part, then this cooperative, and not the individual farmer, is the
producer.
• If the farmer delivers apples in bulk in large containers (transport packaging) to a
agricultural cooperation, who then packs the apples into containers (sales packaging) under
the name or trademark of the cooperative, the agricultural cooperative is the producer.
8
The producer definition addresses packaging used in primary production. ‘Primary production’ is
to be understood as ‘the production, rearing or growing of primary products including harvesting,
milking and farmed animal production prior to slaughter’ (3). Packaging material, for example foil
or straps used for hay bales, is only considered to be made available on the market, and thereby
packaging, when the bales are placed on the market and not when it is used in a production process,
in this case on the same farm.
6) When is packaging considered ‘composite packaging’?
If the total mass of materials which are different from the main packaging material constitutes more
than 5% of the total mass of the packaging unit, such packaging is composite packaging, regardless
of whether the total mass of each other packaging material is less than 5% of the total mass of the
packaging unit (Article 3(1), point (24)).
An example of composite packaging is a multilayer flexible packaging of which the main material
is Polypropylene (PP) (83–90%) used for the structural layer and printability. Such packaging
usually uses a barrier layer of aluminium foil or metallized PET (3–4%) to provide oxygen and a
light barrier to preserve freshness. It may also have a barrier made of low-density polyethylene
(LDPE) or ethylene vinyl acetate (EVA) (3–4%) that ensures heat-sealing for airtight closure.
Printing inks and bonding adhesives used for branding and lamination are also used in such
packaging and constitute 1–2% of the total mass. However, they are not taken into account to
determine whether something constitutes composite packaging.
This type of packaging consists of one main packaging material, in terms of weight, and additional
materials which, taken together constitute more than 5% of the total mass of the packaging unit. It
therefore qualifies as composite packaging within the meaning of Article 3(1), point (24), even
where all packaging materials are plastics. In this context, the notion ‘different materials’ should
be understood as referring to different material categories or functional layers (e.g. barriers), rather
than to variants within the same polymer family. For example, polymer grades or variants within
(3) Article 3(17) of Regulation (EC) No 178/2002 of the European Parliament and of the Council of
28 January 2002 laying down the general principles and requirements of food law, establishing the
European Food Safety Authority and laying down procedures in matters of food safety (OJ L 031
1.2.2002)
9
polyethylene (such as LDPE, LLDPE or HDPE) would normally be considered the same material
for the purposes of this assessment, whereas the combination of polypropylene with polyethylene
layers, aluminium foil or metallised materials would constitute the use of different materials. This
interpretation is without prejudice to the classification of packaging formats set out in Annex II,
Table 1, which serves a different purpose and does not limit the scope of the legal definition of
composite packaging laid down in Article 3. Further details will be provided in the implementing
legislation under Article 7(8).
If the packaging consists of components of different materials that can be manually separated, it is
not considered a composite packaging. The definition of composite packaging is without prejudice
to Directive (EU) 2019/904 (4).
7) Are crown corks for beverage bottles an integrated or separate component?
Crown corks for glass bottles are considered separate components, as per Article 3(1), point (44),
of the Regulation. Such closures, which are not permanently attached to the bottle, need to be
separated completely and permanently from the main packaging unit in order to access the product
and, therefore, to ensure the functionality of the packaging unit. The future delegated act on design
for recycling (DfR) will further specify the rules for integrated and separate components.
8) Are the derogations provided for in Directive 2008/68/EC (5) applicable to all
packaging that is used for the transport of dangerous goods? Are the derogations also
applicable to the transport of non-dangerous goods?
The provisions on recyclability, recycled content and reuse targets contain specific exemptions for
packaging used for transport of dangerous goods. If the packaging is used for transport of
dangerous goods in accordance with Directive 2008/68/EC, even though it does not require UN
approval, e.g. packaging used under limited quantities (LQ) marking, the PPWR derogations are
applicable.
For UN approved packaging used for the transport of non-dangerous goods, the PPWR derogations
do not apply, which means the general rules apply.
(4) Directive (EU) 2019/904 of the European Parliament and of the Council of 5 June 2019 on the reduction
of the impact of certain plastic products on the environment (SUPD).
(5) Directive 2008/68/EC of the European Parliament and of the Council of 24 September 2008 on the
inland transport of dangerous goods (OJ L 260, 30.9.2008, pp. 13–59).
10
III. SUBSTANCES OF CONCERN
1) In the definition of Substances of Concern (SoC), which refers to the ESPR, should
the conditions in Article 2(27) points (a), (b), (c), (d) of the ESPR be considered as
cumulative? How should the wording ‘negatively affects the reuse and recycling of
materials in the product in which it is present’ be understood?
It is sufficient that only one of the conditions under points (a) to (d) of Article 2(27) ESPR is
fulfilled for a substance to be considered as a SoC (6).
As regards the meaning of the wording ‘negatively affects the reuse and recycling…’ the
Commission and the European Chemicals Agency (ECHA) are currently conducting a study on
identifying the SoC that could affect human health and impact packaging reusability and
recyclability.
2) What is the difference between substances and substances of concern (SoC)? Does
the Ecodesign for Sustainable Products Regulation (ESPR) and the PPWR address
substances of concern (SoC) in the same manner?
The definition of substances of concern (SoC) refers to the ESPR (Article 3(1), fourth paragraph
of the Regulation), which means that substances of concern are defined in the same manner in the
PPWR and the ESPR. The ESPR establishes the criteria for identification of substances of concern.
They are mainly based on their hazardous properties and classification in accordance with the CLP
Regulation (7) but also include a reference to negative effects on the reuse and recycling of
materials in the product in which they are present (8). The conditions are not cumulative, which
means that if one of the conditions is fulfilled, the substance is considered as SoC.
3) How will the PPWR deal with the addition of substances of concern (SoC) and the
use of recyclates?
The objective of the Regulation is the minimisation of the presence of SoC in packaging. This will
be done via the identification of substances of concern, as a first step, and their limitation, if they
(6) The ESPR FAQ can be found here: Circabc.
(7) Regulation (EC) No 1272/2008 of the European Parliament and of the Council of 16 December 2008 on
classification, labelling and packaging of substances and mixtures, amending and repealing Directives
67/548/EEC and 1999/45/EC, and amending Regulation (EC) No 1907/2006 (OJ L 353, 31/12/2008, p.
1–1355).
(8) According to Article 2, point (27) of ESPR, ‘a substance of concern’ means a substance that:
a) meets the criteria laid down in Article 57 of Regulation (EC) No 1907/2006 and is identified in
accordance with Article 59(1) of that Regulation;
b) is classified in Part 3 of Annex VI to Regulation (EC) No 1272/2008 in one of the following hazard
classes or hazard categories:
a. carcinogenicity categories 1 and 2;
b. germ cell mutagenicity categories 1 and 2;
c. reproductive toxicity categories 1 and 2;
d. endocrine disruption for human health categories 1 and 2;
e. endocrine disruption for the environment categories 1 and 2;
f. persistent, mobile and toxic or very persistent, very mobile properties;
g. persistent, bioaccumulative and toxic or very persistent, very bioaccumulative properties;
h. respiratory sensitisation category 1;
i. skin sensitisation category 1;
j. hazardous to the aquatic environment — categories chronic 1 to 4;
k. hazardous to the ozone layer;
l. specific target organ toxicity — repeated exposure categories 1 and 2;
m. specific target organ toxicity — single exposure categories 1 and 2.
c) is regulated under Regulation (EU) 2019/1021; or
d) negatively affects the reuse and recycling of materials in the product in which it is present.
https://circabc.europa.eu/ui/group/418195ae-4919-45fa-a959-3b695c9aab28/library/25c48e7c-9ce3-41cb-96ac-d2942a8a29d6/details?download=true
11
are relevant for recycling, via the DfR criteria, to be adopted under Article 6(4) PPWR, or via the
update of REACH restrictions for substances that affect human health or the environment. The
identification of the relevant substances is on-going via a study lead by the Commission and the
European Chemicals Agency (ECHA).
4) How many substances could fall under the definition of substances of concern
(SoC)?
There is no definite number or list of substances of concern (SoC) in packaging. The study, which
the Commission and ECHA are undertaking to comply with its implementation obligation
established in Article 5(2), will look into this issue and will provide a list of SoC on the basis of
the information currently available about packaging manufacturing and waste treatment. There are
several sources of information that can be consulted for each criterion listed in Article 2(27) of
Regulation (EU) 2024/1781 (ESPR) to identify Substances of Concern (e.g. the ‘Candidate list of
Substances of very high concern for Authorisation’ managed by ECHA (9); Annex VI of Regulation
(EC) No 1272/2008 on classification, labelling and packaging of substances and mixtures (10) could
be also used as a source for identifying SoCs.
5) How is the supplier of packaging obligated to comply with the data requirements of
substances of concern (SoC)?
Obligations of packaging suppliers are detailed in Article 16 PPWR. Accordingly, suppliers must
provide the manufacturer with all the information and documentation necessary for the
manufacturer to demonstrate the conformity of packaging and the packaging materials with this
Regulation, either in paper or in electronic format. Manufacturers need this information from
suppliers of packaging materials or converters in order to identify PFAS or other SoC present in
packaging and draft the declaration of conformity demonstrating compliance with Article 5 PPWR.
6) At which value are the concentration limits for SoC set?
The Regulation includes an obligation to minimise the SoC content in material and emissions. The
main driving principle is that human health and environment are protected, i.e. unacceptable
adverse effects should be avoided. The Regulation does not set a general concentration limit for
SoC. Nevertheless, specific concentration limits are established for certain substances (e.g. PFAS
and certain heavy metals).
More information and knowledge on SoC are expected to come from the on-going Commission
and ECHA-led study. But substances meeting the substances of concern (SoC) criteria can already
be identified by the manufacturer based on the existing definition of SoC. The SoC criteria refer
mainly to hazardous properties but also include, on a case-by-case basis, considerations related to
recycling and re-use.
The possibility to establish new concentration limits for SoC in packaging may result from the
evaluation to be carried out by the Commission by 2033, which will consider if the Regulation has
sufficiently contributed to minimising the presence and concentration of SoC in packaging.
Moreover, the Commission may adopt delegated acts in accordance with Article 6(4) to limit the
presence of SoC that negatively affect recycling.
7) What is the implementation date for Article 5(1) PPWR?
(9) https://echa.europa.eu/candidate-list-table.
(10) Regulation (EC) No 1272/2008 of the European Parliament and of the Council of 16 December 2008 on
classification, labelling and packaging of substances and mixtures, amending and repealing Directives
67/548/EEC and 1999/45/EC, and amending Regulation (EC) No 1907/2006 (OJ L 353, 31.12.2008, pp.
1–1355).
https://echa.europa.eu/candidate-list-table
12
The Regulation and therefore the obligation to minimise SoC content will apply from 12 August
2026. Already PPWD contained the obligation to minimise substances of concern with regards to
their presence in emissions, ash or leachate when packaging or its packaging waste residues are
incinerated or landfilled and has set specific concentration limits for four heavy metals (lead,
cadmium, mercury and hexavalent chromium).
8) Is the harmonised standard, EN 13428:2004 still applicable to ensure conformity
with the requirements as regards SoC?
These requirements concerning SoCs have been strengthened in the PPWR. Under the PPWR,
packaging must be manufactured so that the ‘presence and concentration of substances of
concern’, both in the material itself and in emissions or waste outcomes, is minimised. It also
explicitly ties these requirements to effects on reuse, recycling and chemical safety rather than
merely end-of-life disposal. EN 13428 focuses primarily on minimising dangerous substances in
emissions and disposal, not on the holistic lifecycle impacts, as required by Article 5 of the PPWR.
Furthermore, the standard does not reflect the expanded hazard scope of the PPWR covering
SVHCs under REACH, CLP hazard classes and recyclability impacts. Therefore, Annex C of the
existing harmonised standard, EN 13428:2004(11) related to the ’minimisation of dangerous
substances or preparations and demonstration of conformity’, ca therefore no longer create a
presumption of conformity after 12 August 2026. The report on the presence of substances of
concern in packaging, under preparation by the European Chemicals Agency (ECHA), will help
packaging manufacturers to identify substances of concern in packaging and minimise their
presence in packaging’.
9) Does the obligation to minimise the presence of substances of concern (SoC) in
packaging apply to all economic operators?
The obligation applies to all packaging placed on the market, according to the definition in the
Regulation (Article 3(1), point (10)). The manufacturer placing packaging on the market or a
supplier, in case a manufacturer is a microenterprise, must make sure that the provisions are
complied with.
10) When does the obligation on minimisation of substances of concern (SoC) start to
apply for packaging that is not food-contact sensitive?
The general obligation to minimise SoC in Article 5(1) and the limits on four heavy metals in
Article 5(4) apply to all packaging from 12 August 2026. The limits set in Article 5(5) for PFAS
will apply to food-contact materials only.
11) Member States may submit data on a substance they believe to be of concern before
31 December 2025. If Member States inform the Commission about new substances
of concern, will this information be accessible before the Commission delivers its
report in 2026?
According to Article 5(2) of the PPWR, Member States should inform the Commission about
relevant information on SoC before 31 December 2025. This information will be considered in the
development of the study. The monitoring of SoC is a permanent task for the Commission.
(11) Harmonised standards published in Commission communication in the framework of the
implementation of the European Parliament and Council Directive 94/62/EC of 20 December 1994 on
packaging and packaging waste (OJ C 44 of 19 February 2005), EN 13428:2004 ‘Packaging –
Requirements specific to manufacturing and composition – Prevention by source reduction’.
https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:52005XC0219(02)
https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:52005XC0219(02)
https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:52005XC0219(02)
13
12) Does the derogation for glass packaging introduced by Commission Decision
2001/171/EC (12) in relation to heavy metal concentration levels in packaging and
packaging waste continue to apply?
Commission Decision 2001/171/EC continues to apply and has not been repealed by the PPWR.
This means that the packaging may exceed the concentration limit of 100 ppm by weight for the
sum of lead, cadmium, mercury and hexavalent chromium, when this exceedance is due to the
addition of recycled glass. No lead, cadmium, mercury or hexavalent chromium is allowed to be
intentionally introduced during the manufacturing process. The Commission may adopt delegated
acts to amend the limit established in Article 5(4), but only to lower the permitted sum of
concentration levels. The Commission is not empowered to extend the application date of the
heavy-metal restrictions laid down in the PPWR.
13) Will Regulation (EC) 1935/2004 on food contact materials, Regulation (EU)
10/2011 (13) on plastic articles intended to come into contact with food, Regulation
(EU) 2019/1021 on persistent organic pollutants and the REACH regulation be
amended by reference to the PPWR's ban on PFAS?
The PPWR does not establish a PFAS ban but rather sets maximum concentration levels. Also, it
is not provided that the PFAS limits in the PPWR would be taken over into other, ‘vertical’, EU
legislations. Based on Article 5(5), the Commission will carry out an evaluation to assess the need
to amend or repeal the PFAS restriction in the PPWR in case of identified overlaps with restrictions
or prohibitions on the use of PFAS under the FCM Regulation, the REACH Regulation or the POPs
Regulation.
14) Do the PFAS restrictions in Article 5(5) apply both to intentionally added and
unintentionally present PFAS?
The PFAS restriction adopted by the PPWR does not differentiate between intentionally added and
unintentionally present PFAS. Therefore, the provisions in Article 5(5) apply to both. To be noted,
preliminary PFAS laboratory analyses results on a number of selected packaging (14) showed that
in practice only packaging where PFAS have been intentionally added would give results above
the PFAS limit values.
15) Do the restrictions apply only to materials used in packaging manufacturing or also
to the materials and the associated inks, varnishes, glues and adhesives?
The limits apply to the packaging unit as a whole, including the associated inks, varnishes, glues
and adhesives placed on the market by the manufacturer. The latter is the person responsible for
drawing the technical documentation needed to prove compliance (for further information, see
Commission guidance document).
16) Will a list of the PFAS concerned by the ban (with CAS numbers for identification)
be published?
A list of PFAS subject to this restriction will not be published. The limits apply to all PFAS falling
under the definition provided in the PPWR and possibly contained or contaminating the packaging.
(12) Commission Decision of 19 February 2001 establishing the conditions for a derogation for glass
packaging in relation to the heavy metal concentration levels established in Directive 94/62/EC on
packaging and packaging waste (OJ L 62, 2.3.2001, pp. 20–21).
(13) Commission Regulation (EU) No 10/2011 of 14 January 2011 on plastic materials and articles intended
to come into contact with food (OJ L 012 15.1.2011)
(14) Skedung L.1 and Bjarnemark F.1: A Harmonized Workflow for PFAS Compliance Testing under EU
Packaging and Packaging Waste Regulation and Emerging Universal Restrictions: A Food Contact
Packaging Case Study. 1RISE Research Institutes of Sweden
14
17) How will the PFAS limits be enforced, considering there are no harmonised
methodologies for PFAS in food-contact packaging at EU level?
As explained in the Commission guidance document, the Commission is striving to ensure a
harmonised approach of the national market surveillance authorities for the enforcement of the
PFAS limits. There are intense works ongoing involving industrial stakeholders, civil society
associations and the competent authorities in the Member States aiming to deliver a harmonised
testing protocol for PFAS in food-contact packaging. This work stream includes engaging with the
EURL on Food Contact Materials, which coordinates the network of national reference laboratories
for food contact materials.
18) As the starting point for enforcement of the PFAS limits seems to be the total fluorine
analysis, what laboratories offer such testing methodology?
There are already plenty of commercial and university laboratories offering Total Fluorine / Total
Organic Fluorine analysis. It can be expected that many other commercial and accredited
laboratories will in view of the PPWR PFAS limits invest into testing capacities, and that those
already doing it increase theirs.
15
IV. RECYCLABILITY
1) In the context of recyclability performance grade assessment:
• how is a packaging unit defined,
• what is the difference between integrated and separate components, and
• what is the main body of the packaging unit?
A ‘unit of packaging’ is defined in Article 3(1), point (45), of the Regulation as a unit, including
any integrated or separate components, which as a whole serves a packaging function, such as the
containment, protection, handling, delivery, storage, transport or presentation of products. A unit
of packaging is independent from units of grouped or transport packaging where the latter are
discarded prior to the point of sale. The term ‘unit of packaging’ should be considered equal to
‘packaging unit’, which is a term also used in the PPWR. Integrated and separate components are
also defined in the Regulation, in Article 3(1), points (43) and (44), respectively.
An illustrative example of a packaging unit is a plastic ketchup bottle made available to consumers
at the point of sale. Such a ketchup bottle consists of the following packaging components: plastic
bottle, removable lid (i.e. peelable foil), which is typically fully removed by consumers to access
the product, label, and the closure system. If a removable lid needs to be fully completely and
permanently separated by consumers to access the ketchup, then it should be considered as a
separate component. As regards the closure system, it typically does not need to be completely and
permanently separated by consumers and is thus disposed of together with the ketchup bottle.
Assuming that the closure system on a ketchup bottle is not meant to be separated by consumers,
it should be considered as an integrated component. As for the label, it is typically attached to the
plastic bottle and disposed of together with a ketchup bottle. Hence, it is considered an integrated
component; in this context, the plastic bottle itself is the main body of the packaging unit.
Against this background, it could be considered that the main body of the packaging unit is the
packaging part of the packaging unit with the highest share, by weight, except closure on flexible
packaging.
According to Article 6(9), ‘where a unit of packaging includes integrated components, the
assessment of compliance with the design for recycling criteria and with the recycled-at-scale
requirements shall include all integrated components. A separate assessment shall be carried out
for integrated components that can become separated from each other as a result of mechanical
stress during transportation or sorting’.
2) If there is no recyclable alternative for a specific packaging or its components on the
market, could such packaging or its component get an exemption under Article 6?
The exemptions from the recyclability obligations are listed in Article 6(11). The Commission is
not empowered to grant any further exemptions. However, in case of innovative packaging, as
brought to the attention of the competent authorities in the Member States, the Commission must
assess the requests from the competent authorities and update or adopt new delegated acts under
Article 6(4). Innovative packaging is defined as ‘packaging that is manufactured using new
materials, resulting in a significant improvement in the functions of the packaging, such as the
containment, protection, handling, or delivery of products, and in overall demonstrable
environmental benefits, with the exception of packaging that is the result of modification to existing
packaging for the main purpose of improving the presentation of products and marketing’ (Article
3(1), point (46)).
16
The Commission will monitor the impact of the derogations contained in Article 6(11) and
derogations as regards innovative packaging contained in Article 6(10), and may propose
amendments to the Regulation, if necessary.
Therefore, if a packaging or its components does not fall under the established exemptions in
Article 6(11), and does not qualify as innovative packaging, the manufacturers must improve
packaging design to be compliant with the DfR guidelines from 2030 or two years after the entry
into force of the delegated acts adopted under Article 6(4), specifying DfR requirements. Non-
recyclable integrated components may lower the recyclability grade of a unit of packaging or may
even make the entire packaging unit non-compliant.
3) What is the process for granting the derogation and what are the expected timelines
for its completion? What specific criteria does the Commission use to assess
innovativeness?
The process is outlined in Article 6(10). Member States enjoy a margin of discretion implement
the process in their national legislation while respecting the rules outlined in that provision.
The criteria are outlined in Article 3(1), point (46), and the Commission is currently not envisaging
the adoption of further guidance in this regard. Manufacturers using this exemption from the
recyclability requirements must evidence compliance with these criteria in the technical
documentation.
4) Can Member States apply their own eco-modulation criteria?
Under Article 6(4)(d), the Commission will outline a framework concerning the modulation of
financial contributions based on the packaging recyclability performance grades to be paid by
producers to comply with their EPR obligations set out in Article 45(1).
This harmonised framework is necessary to ensure the proper functioning of EU internal market,
by preventing regulatory fragmentation and ensuring legal uncertainty for economic operators, in
particular those placing packaging on the market in several Member States, while at the same time
incentivising more sustainable packaging design. Divergent national eco-modulation schemes
based on recyclability performance could otherwise create obstacles to trade and distort
competition within the internal market.
The harmonised framework will not set the actual amounts of such fees but will instead harmonise
the criteria for the modulation of EPR fees based on the recyclability performance grade obtained
through the recyclability assessment. Until the entry into force of the harmonised eco-modulation
rules, Member States will remain able to eco-modulate fees based on the recyclability of packaging
in accordance with their national provisions adopted under the PPWD. In doing so, Member States
must consider the potential impact of such measures on the internal market. Where national eco-
modulation measures constitute technical regulations or rules affecting products, they must be
notified to the Commission in accordance with Directive (EU) 2015/1535 (15) through the TRIS
notification system.
Following the entry into force of the delegated act on design for recycling, which will establish a
harmonised framework for eco-modulation of EPR fees based on packaging recyclability
performance grade, Member States will be required to apply this harmonised framework. This
obligation aims to ensure the consistent application of eco-modulation rules across the Union and
to safeguard the free movement of goods.
(15) Directive (EU) 2022/2555 of the European Parliament and of the Council of 14 December 2022 on
measures for a high common level of cybersecurity across the Union, amending Regulation (EU)
No 910/2014 and Directive (EU) 2018/1972, and repealing Directive (EU) 2016/1148, (OJ L 333
27.12.2022)
17
However, Member States will continue to be able to eco-modulate financial contributions of
producers on the basis of other criteria, such as recycled content, the presence of substances of
concern, or the reusability of packaging. If Member States decide to introduce eco-modulation
based on the presence of recycled content in plastic packaging, they will be required to take into
account sustainability criteria of recycling technologies and the environmental cost, which are to
be developed by the Commission under Article 7(9) by the end of 2026.
5) If Member States do not reach the recycling targets, is there any mechanism foreseen
to take this into account in the recyclability ‘at scale’ assessment?
The ‘at scale’ assessment will be based on a recycling target of 55% (16) to be achieved at EU level
per packaging categories listed in Table 2 of Annex II. The Commission is empowered to amend
the list of these categories to adapt them to the technical and scientific developments regarding
packaging and packaging waste management. The ‘at scale’ assessment is not based on the
recycling rates achieved at national level and therefore there is no need for a specific mechanism
in the recyclability at scale assessment, which would take into account the fact that a specific
Member State did not reach specific recycling targets.
However, it is important that all Member States strive to optimise their collection, sorting and
recycling systems to improve the overall recycling rate at the Union level and the availability of
secondary feedstock. The Regulation provides for several support measures, such as the obligation
to set up deposit and return systems, mandatory harmonised waste sorting labels, the obligation on
Member States to establish mandatory collection targets, and the prohibition to landfill or
incinerate recyclable packaging. The implementation of these requirements will help increase the
overall recycling rate in the EU and thus allow economic operators to fulfil the recycling ‘at scale’
requirement.
6) What is the scope of the exemption under Article 6(11)(e) for baby food?
The exemption for baby food as referred to in Regulation (EU) No 609/2013 (17) should be
understood in line with the definition given in its Article 2(2f). Therefore, the exemption should
not be understood as covering all fruit juices and purees and other products that are marketed for
consumption by babies.
7) Will the recyclability ‘at scale’ assessment be based on all packaging waste generated
regardless of its origin, sector or type?
The recyclability ‘at scale’ assessment and the related 55% recycling target for all packaging
materials and 30% for wood indeed refers to all plastic packaging waste generated and recycled in
the EU, regardless of its origin (household, commercial and industrial waste), sector or type.
Calculation of the recycling rate should be based on the existing rules for the calculation of
recycling rates laid down in Commission Decision 2005/270, as amended, which will be replaced
by a new decision under Article 56(7) PPWR.
8) Does Article 6 apply to reusable sales and transport packaging placed on the EU
market prior to the entry into force of the requirements under Article 6(1) PPWR?
(16) For all materials except for wooden packaging, where it is 30%.
(17) Regulation (EU) No 609/2013 of the European Parliament and of the Council of 12 June 2013 on food
intended for infants and young children, food for special medical purposes, and total diet replacement
for weight control and repealing Council Directive 92/52/EEC, Commission Directives 96/8/EC,
1999/21/EC, 2006/125/EC and 2006/141/EC, Directive 2009/39/EC of the European Parliament and of
the Council and Commission Regulations (EC) No 41/2009 and (EC) No 953/2009 (OJ L 181,
29.6.2013, pp. 35–56)
18
Recital (14) explains that ‘packaging should be placed on the market only if it complies with the
sustainability requirements and labelling requirements laid down in or pursuant to this Regulation’
(emphasis added). Packaging already placed on the Union market before the date of application of
relevant requirements, including packaging in the stocks, does not need to meet the sustainability
and labelling requirements laid down in or pursuant to this Regulation and does not need to be
withdrawn.
Article 6(2) requires that all packaging placed on the market 24 months from the date of entry into
force of the delegated acts adopted pursuant to Article 6(4) is recyclable according to the DfR
principles laid down therein. This obligation refers to every type of packaging, regardless of
whether it is reusable or single-use, or sales, grouped or transport packaging.
Therefore, since the delegated acts under Article 6(4) are to be adopted by 1 January 2028, reusable
or transport packaging which manufacturers will have placed on the market before 1 January 2030,
can stay on the market even if it is not compliant with the recyclability requirements. Placing on
the market refers to every single packaging unit and not to the packaging design.
9) Are the exemptions from the recyclability requirements for packaging made from
cork, lightweight wood, textile, ceramics rubber, porcelain and wax valid until 2035?
Article 6(1) requires that all packaging be recyclable. Article 6(11) establishes exemptions from
this requirement for certain packaging materials and sectors. The Commission will review these
exemptions by 1 January 2035 to consider if it is appropriate to maintain them. Based on this
assessment, it may propose to amend or remove them.
The exceptions for packaging made from cork, lightweight wood, textile, ceramics rubber,
porcelain and wax apply only to sales packaging and mean that such packaging will not have to
undergo the recyclability assessment for the purpose of determining if it can be placed on the
market.
However, the obligation to adjust the EPR fees based on the recyclability performance will apply
also to such sales packaging. The recyclability assessment for such packaging will thus be carried
out only for the purpose of determining the EPR fee modulation.
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V. RECYCLED CONTENT IN PLASTIC PACKAGING
1) How should compliance with the recycled content requirements be demonstrated?
Compliance with the recycled content targets in the PPWR must be demonstrated in the technical
documentation for the packaging as specified in Annex VII. Compliance with the recycled content
requirements can be exemplified as follows.
An economic operator places a plastic tray made of polyethylene (PET) with a peelable lid made
of polypropylene (PP) on the market. In this case, we could assume that the PET tray and PP lid
are manufactured in different manufacturing plants within the EU and supplied to the economic
operator who assembles the packaging components into a tray with a lid, fill it with product, and
eventually places it on the market.
The two manufacturing plants which manufacture, respectively, the tray and the lid must each
disclose information about the compliance with the minimum recycled content requirements for
their components, as provided for in Article 7(2). Based on the information from these
manufacturing plants, the economic operator who eventually places the tray with the lid on the
market (i.e. the manufacturer), must draw up the technical documentation that demonstrates
compliance with the legal requirements for recycled content.
The same principle applies to intermediate plastic packaging components, empty plastic packaging
or filled plastic packaging imported into the EU. The economic operator must also ensure that the
requirements for the recycled content meet the sustainability and equivalence criteria, which will
be set out in the implementing acts pursuant to Article 7(9) and (10), respectively.
2) What is to be understood by ‘average per manufacturing plant and year’ in the context
of recycled content in plastic packaging?
A manufacturing plant must be understood as the industrial facility in which packaging is
manufactured. An average per year refers to the amount of recyclates (recycled content) in each
plastic packaging type and format over the period of a calendar year, produced for each
manufacturer in a specific manufacturing plant. The manufacturing plant will have to provide
documentation demonstrating that the average supply per year to the specific manufacturer fulfils
the targets for recycled content.
Manufacturers usually produce several packaging formats in one manufacturing plant and will
therefore have to calculate the recycled content targets for each packaging type and format.
The implementing act to be adopted under Article 7(8) will outline the rules on how to calculate
and verify the recycled content in plastic packaging.
3) Are adhesives, paints and inks covered by the recycled content requirements for
plastic packaging?
Adhesives, paints and inks are not deemed plastic under the PPWR and therefore do not need to
fulfil the recycled content requirements. This is regardless of whether they represent less than 5%
of the packaging unit.
4) Are environmental claims on recycled content in plastic packaging allowed?
Environmental claims on recycled content in plastic packaging are allowed where the recycled
content exceeds the applicable minimum requirements set out in Article 7(1) and (2) of the PPWR.
Article 14 specifies that the economic operator is allowed to make environmental claims for a
packaging unit, the part of the packaging unit that contains the recycled content, or all packaging
placed on the market over a calendar year by the economic operator. This is exemplified in the
table below.
20
Example PPWR recycled
content
requirements
Environmental
claim for:
Allowed environmental claim
PET plastic bottle
with a closure system
made of PP
PET bottle: 30%
PP closure: 10%
Packaging unit
(bottle and a
closure system)
The recycled content exceeds
30% for the PET bottle or 10%
for the PP closure system.
Regardless of the choice to make environmental claims or not, compliance with the legal
requirements must be demonstrated in the technical documentation.
5) How do economic operators know which recycled content requirements to fulfil?
The recycled content requirements apply to sales, grouped, and transport plastic packaging. Firstly,
the economic operator must determine whether the packaging is contact-sensitive. Secondly, the
economic operator must determine what polymer the packaging is made from. Based on this
information, the economic operator can then determine what recycled content requirements to
fulfil.
This logic is illustrated in the following table.
Packaging
format
1st step: Is the
packaging
contact-
sensitive?
2nd step: What
is the polymer
made from?
2030 applicable
target
Example A Pallet wrapping
film to transport
goods
Non-contact
sensitive
Other than PET Art. 7(1)(d), 35%
Example B Beverage carton Contact-sensitive Other than PET Art. 7(1)(b), 10%
Example C Single-use
plastic beverage
bottle:
Contact-sensitive PET Art. 7(1)(c, 30%
6) Do the requirements for recycled content apply to packaging placed on the market
before 2030?
The recycled content requirements apply only to packaging placed on the market from 1 January
2030 or three years after entry into force of the implementing act in Article 7(8), whichever is the
latest. However, no exhaustion of stocks is envisaged for packaging supplied to manufacturers and
not yet placed on the market by the latter before the due date.
7) Will also a plastic cap and a label on a glass bottle need to comply with the recycled
content requirements?
Article 7(5)(b) exempts plastic parts that represent less than 5% of the total weight of a packaging
unit from the recycled content requirements. This exemption applies exclusively to plastic parts
and does not extend to non-plastic materials.
By way of example, in the case of a glass bottle with a metallic cap and a label, the metallic cap is
not a plastic part and therefore falls outside the scope of the recycled content requirements. A
21
plastic label, however, is exempted only if its weight accounts for less than 5% of the total weight
of the packaging unit, the bottle.
8) Recycled plastic in plastic caps is mandatory for milk but not for infant formula
packaging. Must an economic operator that uses the same caps for these products
meet the targets for recycled plastic content to comply with the requirements for milk
packaging?
As of 2030, manufacturers must ensure that the plastic part of the packaging placed on the market
is compliant with the recycled content targets of Article 7(1).
Milk is not exempted from the recycled content requirements. Therefore, a manufacturer must
ensure that plastic caps that are used for the milk packaging fulfil the recycled content
requirements. On the other hand, plastic caps for instant baby formula are not required to include
recycled content due to the exemption set out in Article 7(4), point (g).
9) Is there a difference between ‘contact-sensitive plastic packaging’ and ‘immediate
packaging’ as used in the exemptions of Article 7?
The term ‘immediate packaging’ refers to the ‘(…) packaging immediately in contact with the
medicinal product’ (18), whereas according to Article 3(1), point (49), of the PPWR contact-
sensitive packaging means packaging that is intended to be used for food and medicinal products.
In the context of medical devices and other medicinal products ‘immediate packaging’ will
generally qualify as ‘contact-sensitive plastic packaging’ according to Article 3(1), point (49), of
the PPWR, and while the concepts are not identical, they should be understood in the same way
for the purpose of implementation of Article 7 of the PPWR.
10) Could the Commission clarify the reporting obligations related to recycled content
under the PPWR and SUPD and their interplay?
Article 6(5), points (a) and (b) of SUPD (i.e. recycled content targets for beverage bottles listed in
Part F of Annex to SUPD), and Article 13(1)(e) on related Member States’ reporting remain in
force until 1 January 2030 or 3 years after the entry into force of the implementing act on the
calculation of recycled content referred to in Article 7(8).
There are some differences in scope between the PPWR and the SUPD, which should be taken into
account:
• In the SUPD, the target is at Member State level, whereas the PPWR sets the. requirements
per packaging type/format, calculated as an average per manufacturing plant and year.
• There is no minimum threshold in the SUPD for composite materials, whereas the PPWR
contains an exemption for the plastic part if it represents less than 5% of packaging unit
weight.
• There is no exemption regarding compostable plastic packaging in the SUPD.
11) Recycled content requirements for imported plastic packaging
Regulation (EU) 2022/1616 and its provisions (especially Article 6) apply to all recycled plastics
for food contact materials placed on the EU market, including imported packaging.
Therefore, importers of plastic materials with recycled content that intend to use this material as
food-contact material, including food-contact packaging, should ensure that these materials comply
(18) Article 1(23) of Directive 2001/83/EC of the European Parliament and of the Council of 6 November
2001 on the Community code relating to medicinal products for human use (OJ L 311 28.11.2001, p.
67)
22
with the requirements outlined below. If not compliant, these materials may not be placed on the
market for food contact applications, including food-contact packaging. However, they may be
used for other purposes. Article 6 of that Regulation mandates the following:
• Separate collection of plastic waste;
• A certificate obtained with third-party certification of the pre-processing activities in
accordance with Article 6, including all activities from sorting to recycling of plastic
waste;
• Proof that the recyclates have been produced in accordance with Regulation (EU)
10/2011.
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VI. COMPOSTABILITY
1) Article 9(1) mandates a compostability requirement for certain packaging types. Will
these packaging types be allowed in the bio-waste stream even before 12 February
2028?
Indeed, the Regulation changed the definition of packaging to include tea and coffee bags which
are not left empty after use. Such new packaging items will be classified as packaging when the
Regulation becomes applicable, that is on 12 August 2026.
As Article 9 on compostability applies from 12 February 2028, Member States are not required to
accept such packaging in the bio-waste steam before that date, but they are encouraged to accept
them.
2) How should manufacturers deal with the fact that not all industrial composting
facilities operate in accordance with EN 13432:2000? Will waste management
operators in all Member States have to accept compostable packaging if it is certified
according to the harmonised standard EN 13432:2000?
While the Regulation does not state explicitly that composting facilities must operate in accordance
with the harmonised standard, the Commission expects that this will indeed be the case. For
example, Article 9(2) conditions the Member States’ flexibility to add additional packaging items
to the national lists of mandatorily compostable packaging to the existence of ‘appropriate waste
collection schemes and waste management infrastructure to ensure that compostable packaging
enters the bio-waste management stream’. The Commission will ensure that associations
representing industrial composting will be fully involved in the development of the updated
industrial compostability standards.
3) If a product is nowadays compostable, and on the market, can economic operators
continue to market it after the Regulation has entered into force and become
applicable?
The answer is ‘yes’, if there is a clear legal requirement in the territory of a Member State where
the economic operator is marketing their products that a particular packaging format must be
compostable.
As explained in point 8 of the Commission guidance document, Member States have the possibility
until 12 August 2026 to decide that packaging formats additional to items listed in Article 9(1) and
9(2)(a) must be compostable on their territories.
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VII. PACKAGING MINIMISATION
1) Do both Article 10(1) and (2) on packaging minimisation apply by 1 January 2030?
Yes. Both Article 10(1) and (2) apply by 1 January 2030. Until the end of 2029, the essential
requirements from the PPWD continue to apply and thus also the existing standard EN 2004:13428.
This results from Article 70(1)(b) of the Regulation.
2) How should the term ‘increase the perceived volume of the product’ in Article 10(2)
be understood?
The use of certain packaging characteristics, such as double walls or false bottoms, is not allowed
when the perceived volume of the product is increased.
An illustrative example below is provided to help better understanding.
Example Packaging minimisation Choices that might increase the
perceived volume of the product
Plastic or glass 50 ml jar
for facial cream
Plastic or glass jars are reduced
to the minimum volume
necessary to protect the
product inside
Use of double walls or false bottoms to
make it appear that the content of the cream
as more than 50 ml
Use of cardboard boxes around the jar
which make it appear that the content of the
cream larger than 50 ml
Moreover, the Impact Assessment that supported the legislative proposal of the PPWR outlines a
few examples on ‘increase the perceived volume of the product’ (19).
Overall, the economic operator must prove that double walls, false bottoms, frontal flaps and
additional layers are used only in circumstances where the packaging functionality cannot be
ensured otherwise and/or in cases where these components add legitimate functionality to the
packaging. This will have to be demonstrated via tests and proven in the technical documentation,
by providing a sufficient justification.
3) How will the requirements of packaging minimisation be enforced for other than the
most common packaging types and formats?
By 12 February 2027, the Commission will request the European standardisation organisations to
prepare or update, as appropriate, harmonised standards laying down the methodology for the
calculation and measurement of compliance with the minimisation requirements. These standard(s)
will be an update of the existing standard EN 13428:2004 to account for the changed performance
criteria set out in Annex IV of the Regulation and will outline the methodology for demonstrating
compliance with the minimisation requirements for all packaging. Once adopted, economic
operators will be able to use the updated standard and thus benefit from the presumption of
conformity with the minimisation requirement.
(19) Assessment of options for reinforcing the Packaging and Packaging Waste Directive’s essential
requirements and other measures to reduce the generation of packaging waste - Publications Office of
the EU, page 26: an identical packaging format in terms of size, weight and volume is used to pack
different amounts of the same type of screws. In the first case, the packaging fits 100 screws, whereas
in the second case the same packaging contains 20 screws of the same size. Therefore, the second case
(i.e. pack of 20 screws) is considered over-packaged, both in terms of the volume and weight of the
pack.
https://op.europa.eu/en/publication-detail/-/publication/bdacd175-a0a9-11ed-b508-01aa75ed71a1
https://op.europa.eu/en/publication-detail/-/publication/bdacd175-a0a9-11ed-b508-01aa75ed71a1
https://op.europa.eu/en/publication-detail/-/publication/bdacd175-a0a9-11ed-b508-01aa75ed71a1
25
In addition, for the most common packaging types and formats, the Commission will request the
European standardisation bodies to prepare standard(s) specifying the maximum adequate weight
and volume limits and, where appropriate, wall thickness and maximum empty space.
4) What are the ‘most common packaging types and formats’ mentioned in Article
10(3)?
The Commission will identify the ‘most common packaging types and formats’ in its forthcoming
standardisation request pursuant to Article 10(3) PPWR.
These types and formats will be identified in collaboration with the industry and other stakeholders
and be based on the available market data in terms of units placed on the market, on a level of
granularity which accounts for the packaging functionality, packaging material and shape, as well
as the packaged product. The potential for minimisation will also be considered in the framing of
the standardisation request.
5) Which packaging is exempted from the minimisation requirements?
The following packaging is excluded from the minimisation requirements (Article 10(2)):
Packaged products or beverages that benefit from a geographical indication protected under Union
law, such as under Regulation (EU) No 1308/2013 for wine, Regulation (EU) 2019/787 for spirit
drinks or Regulation (EU) 2023/2411 for craft and industrial products or is covered by a quality
scheme as referred to in Regulation (EU) 2024/1143.
If packaging design is protected by a Community design pursuant to Council Regulation (EC) No
6/2002 (64) or by design rights falling within the scope of Directive 98/71/EC of the European
Parliament and of the Council (65), including international agreements having effect in one of the
Member States. For the exemption to apply, the packaging design must be protected before
11 February 2025, and the application of the minimisation requirements affect the packaging
design in a way that it would alter its novelty and its individual character
If packaging shape is a trademark falling within the scope of Regulation (EU) 2017/1001 (66) or
Directive (EU) 2015/2436 (67), including trademarks registered under international agreements
having effect in one of the Member States. For the exemption to apply, the trademark must be
protected before 11 February 2025, and the application of the minimisation requirements affect the
packaging in a way that the trademark can no longer distinguish the marked product from those of
other undertakings.
If the economic operator wants to use these exemptions, it will need to provide evidence related to
them in the technical documentation. It will not be sufficient to provide a licencing number. It will
also be necessary to demonstrate the existence and assessment of other conditions.
6) How will the packaging ’shape’ affect the packaging minimisation assessment?
Firstly, the economic operator will have to consider if its packaging is covered by the exemption
in Article 10(2)(a) related to shapes which are protected trademarks and if the conditions set out in
that provision for exemption from the minimisation requirements are fulfilled. The verification of
said conditions needs to be demonstrated by the economic operator.
If the packaging is not covered by the exemption, economic operators will apply the updated
harmonised standard on the methodology for packaging minimisation assessment to be requested
by the Commission pursuant to Article 10(3). This updated harmonised standard will take the
packaging shape into account in its methodology. For example, if a specific shape is necessary to
provide packaging for the packaging functionality, such as safe-handling design, child resistance,
anti-tamper, anti-theft, anti-counterfeit, hazard warnings, or specific product characteristics.
7) What is the relationship between the minimisation requirement in the PPWR and the
ones in the ESPR?
https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=OJ:L_202500040#ntr64-L_202500040EN.000101-E0064
https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=OJ:L_202500040#ntr65-L_202500040EN.000101-E0065
https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=OJ:L_202500040#ntr66-L_202500040EN.000101-E0066
https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=OJ:L_202500040#ntr67-L_202500040EN.000101-E0067
26
The general principle is that acts under the ESPR only take the lead on regulating products when
their environmental sustainability dimensions either cannot or have not been fully and
appropriately addressed by other instruments. This principle applies also to packaging. As
explained in Recital 25 of the ESPR, if needed, the ESPR may complement the PPWR by setting
product-based requirements that focus on the packaging of specific products. The ESPR will not,
however, set general eco-design or sustainability requirements for packaging as a product group
because these requirements are laid down in PPWR.
27
VIII. LABELLING
1) Will labelling requirements for reusable packaging under Article 12(2) apply at the
level of each individual packaging?
Reusable packaging must be designed to ensure a minimum number of rotations, which
will be established in the delegated act to be adopted under Article 11(2). The obligation
to calculate and report on the number of rotations for reusable transport packaging will
depend on the type of reuse system. Namely, open-loop reuse systems without a system
operator are exempted from this obligation and from the obligation to bear a reusable
packaging label and a QR code.
According to Article 12(2), reusable transport packaging circulating within closed-loop
systems will have to bear a reusable packaging label and a QR code or another standardised
open digital data carrier that will allow for tracking of the individual packaging and the
calculation of its rotations. The detailed rules, including the label informing consumers
that a packaging is reusable, will be clarified in the implementing act to be adopted under
Article 12(6). This act will also specify situations when it is considered that an individual
QR code and tracking of rotations is not feasible and the calculation of rotations can thus be
made based on an average estimation.
2) Under what circumstances are labels, marks, symbols, or inscriptions considered
misleading?
Marks, symbols, labels, or inscriptions should not mislead consumers regarding sustainability
requirements of packaging such as its recyclability, recycled content, reusability, compostability,
bio-based content, hazardous substances content or waste management options (Article 12(8)).
To further understand the notion of misleading claim please refer to Directive (EU) 2024/825 (20)
‘Empowering Consumers for the Green Transition’. Claims are considered misleading if they cause
the consumers to make decisions that they would not otherwise make.
3) Should a packaging bear a national DRS label when it is imported from one Member
State to another?
Labelling of packaging covered by the mandatory deposit and return systems has not been
harmonised in the PPWR. Therefore, products will have to comply with the DRS label of the
Member State where they are made available on the market. Member States may require that such
packaging be marked with a ‘harmonised colour label’ as specified in Article 12(1), fourth
subparagraph. If products are imported in the context of private imports, i.e. directly by the end
user and with no intention to commercialise them, this is not considered ‘making available on the
market’. Member States cannot prohibit the affixing of DRS labels in place in other Member States.
4) Which are the substances of concern that need to be identified by the labelling
requirements in Article 12(7), second subparagraph?
The European Chemicals Agency (ECHA) is currently conducting a study to identify the
substances of concern (SoC) in packaging that could affect human health and those that can impact
packaging reusability and recyclability. Based on this input, the Commission will develop an
implementing act establishing the methodology for labelling of SoC by means of digital labelling.
(20) Directive (EU) 2024/825 of the European Parliament and of the Council of 28 February 2024 amending
Directives 2005/29/EC and 2011/83/EU as regards empowering consumers for the green transition
through better protection against unfair practices and through better information (OJ L, 2024/825,
6.3.2024)
28
IX. ENVIRONMENTAL CLAIMS
1) Will businesses be allowed to make environmental claims about features that are
equivalent to those established by the Regulation?
Article 14 applies only to ‘properties for which legal requirements are set out in this
Regulation’. Environmental claims and sustainability labels related to, e.g., recyclability,
compostability, recycled content, reusability, weight and volume minimisation, fall under the
PPWR and manufacturers will need to make sure that such claims comply with Article 14, i.e.
relate to properties that go beyond minimum requirements set by the PPWR and specifies if the
claim refers to the whole packaging unit or a specific part of it.
As regards environmental claims related to sustainability requirements outside the scope of this
Regulation, for example recycled content in aluminium packaging, they must comply with the
existing EU rules on environmental claims, in particular the Empowerment of Consumers Directive
(EU) 2024/825, which amends the Unfair Commercial Practices Directive (2005/29/EC) and
the Consumer Rights Directive (2011/83/EU). For further information on the relationship between
the Unfair Commercial Practices Directive and other legislation, please, consult the Commission
Guidance document on its interpretation (21), in particular parts 1.2.1. on relationship with other
EU legislation and part 4.1.1.1 on the Interplay with other EU legislation on environmental claims,
which explains that lex specialis (e.g. PPWR) prevails over lex generalis (UCPD) in case of
conflict.
2) In case the manufacturer wants to make a claim about the share of recycled content
on the packaging unit, which threshold should be considered as the minimum
requirement established by law? Will it be possible to make claims about 10, 20 or
50% of recycled content in each unit?
In case a manufacturer makes a claim about the share of recycled content in packaging placed on
the market, the applicable minimum targets (calculated as an average per manufacturing plant and
per year), will apply and the manufacturers will be allowed to make the claim only if the recycled
content exceeds those targets. For recycled content, the calculation and verification methodology
will be established by 31 December 2026 in an implementing act, and environmental claims will
need to comply with these rules. The voluntary label for recycled content will be developed by the
Commission.
3) Does Article 14 apply only for environmental claims which refer to requirements
stated in the PPWR (e.g. recyclability) or also for any other kind of environmental
claims on sustainable packaging?
Article 14 applies only to ‘properties for which legal requirements are set out in this
Regulation’. Therefore, as regards environmental claims which are not regulated under the PPWR,
e.g. related to recycled aluminium content, they must comply with the existing EU rules on
environmental claims, in particular the Empowerment of Consumers Directive (EU) 2024/825.
(21) Commission Notice – Guidance on the interpretation and application of Directive 2005/29/EC of the
European Parliament and of the Council concerning unfair business-to-consumer commercial practices
in the internal market (OJ C 526, 29.12.2021, pp. 1–129).
https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX%3A52021XC1229%2805%29&qid=1640961745514
https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX%3A52021XC1229%2805%29&qid=1640961745514
https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX%3A52021XC1229%2805%29&qid=1640961745514
29
X. OBLIGATIONS OF MANUFACTURERS
1) Article 15(1) states that manufacturers must place on the market only packaging
which complies with the requirements set out in Articles 5 to 12. Does this obligation
apply exclusively to packaging manufacturers?
The obligation to place on the market only compliant packaging does not apply only to economic
operators defined as the manufacturer, but also to importers and distributors.
Pursuant to Article 15(1), ‘manufacturers shall only place on the market packaging which is in
conformity with the requirements laid down in or pursuant to Articles 5 to 12.’ The conformity
assessment procedure (Article 38) can be carried out by the manufacturer or by someone else on
their behalf (e.g. a laboratory or a certification scheme), in accordance with Article 15(2). The EU
declaration of conformity (Article 39) must be drafted by the manufacturer, based on the
information and documentation provided by suppliers pursuant to Article 16(1), or by an authorised
representative, appointed by the manufacturer by a written mandate pursuant to Article 17. This
means that the manufacturer is the sole economic operator bearing legal responsibility for
packaging compliance with the sustainability and labelling requirements, regardless of the fact
who might have actually drafted the EU declaration of conformity or parts of it.
2) When is the effective date of application of Articles 15 and 18 of the PPWR on
obligations of importers and manufacturers?
PPWR will become applicable on 12 August 2026, and this includes provisions on the obligations
of manufacturers and importers. However, these provisions must be read in conjunction with the
substantive obligations, as defined in various provisions of the Regulation, notably in Articles 5 –
12. Some substantive provisions have different application dates, which are often linked to the
adoption of a specific implementing measure by the Commission.
For example, as regards recyclability, manufacturers must comply with the recyclability
requirements and perform the conformity assessment procedure in accordance with Article 38 and
Annex VII of the PPWR only two years from the adoption of the delegated act on design for
recycling requirements. On the assumption that this delegated act will be adopted by the
Commission in January 2028 and will fully harmonise design for recycling requirements and the
related assessment methodology, the binding recyclability performance criteria will only apply
from 1 January 2030 or two years from the date of entry into force of the delegated act.
Other effective dates of application of sustainability and other key requirements under PPWR:
- Recycled content in plastic packaging: 1 January 2030 or three years from the date of entry
into force of the implementing act referred to in Article 7(8) PPWR.
- Minimisation (Article 10(1) – (2)): 1 January 2030.
- Void space requirement for transport, grouped and e-commerce packaging: from 1 January
2030 or three years after the entry into force of the implementing act under Art. 24(2); as
regards void space in sales packaging, see Art. 10.
- Reusable packaging (Art. 11): from the date of entry into force of the Regulation (11
February 2025), but minimum number of rotations will have to be complied with
depending on the date that will be specified in the implementing act referred to in Article
11(2) to be adopted by 12 February 2027.
- Reuse targets: from 1 January 2030 or 18 months from the date of entry into force of the
implementing act on the calculation of reuse targets, referred to in Article 30(3), to be
adopted by 30 June 2027.
30
3) Should suppliers be required to mark ‘plain’ packaging, such as plastic carrier bags,
with a serial number?
Suppliers of packaging or packaging material are not manufacturers according to the definition of
manufacturer in Article 3(1), point (13), except when the ‘manufacturer’ is a microenterprise and
the supplier is located in the same Member State.
The Regulation does not require that suppliers of packaging are identifiable on the packaging or
via a data carrier. They must only ensure that the manufacturer has all the information and
documentation necessary to demonstrate packaging conformity.
The Regulation does not require either that suppliers identify packaging with a type, batch or a
serial number; this is an obligation that falls on manufacturers. However, in practice, it may well
be that it will be the suppliers of packaging who will ensure that packaging is identifiable, as this
is often done at the production stage.
4) Do importers or distributors who supply packaging materials need to comply with
any requirements in the Regulation?
Suppliers do not have the legal responsibility to comply with the Regulation. However, their
clients who place packaging or packaged products on the EU market (manufacturers, importers)
will need to ensure that that they use compliant packaging or packaging material. It is therefore
normal to assume that suppliers that sell non-complaint packaging will lose their clients.
31
XI. EMPTY SPACE
1) Who is the obligated party to comply with the empty space requirements under
Article 24?
Article 24(1) establishes maximum empty space ratio for grouped, transport and e-commerce
packaging which needs to be met by the economic operator who fills such packaging. This may be
the manufacturer as defined in Article 3(1), point (13), as well as other economic operators who
make packaged products available on the market.
2) How should the term ‘minimum necessary’ in Article 24(4) be understood?
The empty space ratio for sales packaging means the difference between the total internal volume
of the sales packaging and the volume of the packaged product. For assessing compliance with this
paragraph, space filled by filling materials, such as paper cuttings, air cushions, bubble wraps,
sponge fillers, foam fillers, wood wool, polystyrene or styrofoam chips, shall be considered as
empty space. For empty space ratio in sales packaging, there is no maximum threshold established
in the PPWR; instead, it is left to the relevant economic operator who fills sales packaging to
minimise the empty space and to demonstrate this in the technical documentation. This provision
should be read in conjunction with Article 10 on packaging minimisation.
3) Are the design patents covered by the 50% empty space ratio requirement?
Contrary to Article 10 on packaging minimisation, Article 24 does not have specific exemptions
for packaging covered by packaging design rights or trademarks. However, the 50% threshold
applies only to grouped packaging, transport packaging and e-commerce packaging (Article 24(1)).
4) How will round products and other irregular shapes be addressed by the
methodology for the calculation of the empty space?
By 12 February 2028, the Commission shall adopt implementing acts to establish the methodology
for the calculation of the empty space ratio for grouped packaging, transport packaging and e-
commerce packaging (Article 24(2)). That methodology shall consider the special characteristics
of packaging which needs to be placed in an empty space that is large enough to comply with the
applicable legal requirements or to protect the product. The methodology shall take into account
packaged products of irregular shape, packaging containing more than one sales packaging or
product, packaging containing liquid products, packaged products the content of which can easily
be damaged and packaged products that can be damaged by larger products due to their small
dimensions, and the minimum space on the transport packaging to enable shipment labels to be
affixed. Economic operators will need to comply with the empty space ratio threshold by 1 January
2030 or 3 years after the entry into force of this implementing act.
The methodology will be based on a wide range of examples, including irregular shapes.
32
XII. BANS AND THE USE OF CERTAIN PACKAGING
1) What instruments are available to ensure legal harmonisation and predictability of
the implementation of Annex V?
The Regulation empowers the Commission to adopt guidelines by February 2027, in consultation
with Member States and EFSA (European Food Safety Authority), to explain Annex V in more
detail, including examples of packaging formats in scope, and any exemptions from the restrictions,
and provide a non-exhaustive list of fruits and vegetables that are excluded from point 2 of Annex
V (Article 25(6) PPWR).
The Commission has started preparatory works for the guidelines and intends to ensure that these
guidelines are based on science and on the latest technological developments. The intention is to
ensure a common understanding and the equal implementation of the packaging formats in scope,
and any exemptions from restrictions. While the Regulation does not empower the Commission to
harmonise the list of exempted fruits and vegetables via an implementing or delegated act, the
Commission, together with EFSA, has been working hard to ensure a solid scientific basis for the
future guidelines, and expects that Member States will follow the guidelines, once published.
Finally, the Regulation contains a specific review clause requiring the Commission to assess, by
2032, the packaging bans and empowering it to propose new restrictions or to amend the existing
derogations and exemptions.
2) What do the terms ‘unprocessed fresh fruits and vegetables’ and ‘demonstrated need’
in point 2 of Annex V mean?
The terms ‘unprocessed fresh fruits and vegetables’ and ‘demonstrated need’ will be further
clarified after the formal consultation with the related stakeholders and EFSA, in the context of the
development of the Commission guidelines.
The term ‘unprocessed fresh fruits and vegetables’ refers to fresh fruit and vegetables that have
not been altered.
When such fruits and vegetables weigh less than 1,5 kg, they cannot be prepacked. The
Commission will develop guidelines explaining, based on scientific studies, which unprocessed
fresh fruit and vegetables are appropriate for exemptions.
3) Is it possible to extend the scope of the illustrative formats and products covered by
point 4 of Annex V to additional sectors (e.g. schools), beyond the exemptions
explicitly listed?
Point 4 of Annex V concerns single-use plastic packaging for condiments, preserves, sauces, coffee
creamer, sugar and seasoning in the HORECA sector. It expressly exempts only (a) take-away
ready-prepared food intended for immediate consumption and (b) the healthcare sector. The
illustrative formats will be developed in the guidelines. The PPWR does not provide a legal basis
to enlarge the list of exemptions to other sectors.
4) How shall the term ‘necessary to facilitate handling’ under point 1 of Annex V to be
understood?
The restriction in question concerns ‘single- use plastic grouped packaging used at the point of
sale (…), designed as convenience packaging to enable or encourage consumers to purchase more
than one product’. What is targeted is unnecessary single-use plastic grouped packaging designed
for ease of use and portability, and which also incites consumers to buy more.
Both conditions should be fulfilled for the ban to apply. The most common examples of such
packaging are collation films and shrink wraps, grouping two or more stock keeping units (SKUs).
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Other examples and other guiding principles will be provided in the guidelines. As regards B2B
situations, they are not covered by the ban.
The Commission guidelines will further specify how the term ‘necessary to facilitate handling’ will
be operationalised, through illustrative examples.
5) Are biodegradable or compostable bags banned by Annex V, point 6?
All very lightweight plastic carrier bags (thus including compostable or biodegradable bags) are
banned under Annex V, point 6. However, if such bags are needed for hygiene purposes or provided
as sales packaging for loose food to prevent food waste, they are excluded from this harmonised
ban.
Very lightweight plastic carrier bags, which are needed for hygiene purposes or provided as sales
packaging for loose food to prevent food waste’, although not banned by Annex V, point 6, are in
principle included in the 40% reduction target set out in Article 34(1) PPWR for all lightweight
plastic carrier bags. However, Member States may decide to exempt that specific type of bag from
the reduction target (Article 34(4) PPWR). To reach the 40% target, Member States may decide to
ban very lightweight plastic carrier bags, including compostable or biodegradable bags, which are
needed for hygiene purposes or provided as sales packaging for loose food to prevent food waste
However, marketing restrictions (bans) by Members States must be proportionate and non-
discriminatory (Article 34(2) PPWR).
6) Can hotel miniature cosmetics be available on demand? Can we expect derogations
for products packaged for hygienic reasons, such as toothbrush and cotton pads?
Annex V, point 5, refers to ‘single-use accommodation sector packaging intended for an individual
booking’.
The Regulation does not define the terms ‘cosmetics, hygiene and toiletry product’, nor does it
exempt miniature packaging available on demand or purchased at the hotel premises, but only
those intended for an individual booking. To ensure a harmonised approach, the Commission is
mandated to explain Annex V in more detail, including examples of the packaging formats in
scope, and any exemptions from the restrictions, by publishing guidelines by 12 February 2027
(Article 25(6) PPWR). The timely adoption of the Commission guidelines will ensure that the
scope of the provision is sufficiently clear almost three years ahead of the application date.
The Commission intends to consult the relevant stakeholders, including the hospitality sector,
before publishing them. Furthermore, it should be recalled that only packaging is banned and not
products as such, which could therefore still be made available without packaging.
7) Will single-use plastic food and beverage packaging be banned from entertainment
and sporting events and festivals?
Sport and entertainment venues and festivals are included in the ‘HORECA’ definition (Article
3(1), point (35)), which refers to ‘Accommodation and Food Service Activities according to NACE
Rev. 2 – Statistical classification of economic activities. NACE Rev. 2 includes guidance which
explains that the decisive element is that meals, including beverages, fit for immediate consumption
are offered at the facility, and not the kind of facility providing them. However, establishments in
the HORECA sector that do not have access to drinking water are expressly exempted from the
ban, pursuant to Annex V, point 3.
8) Is hotel room service covered by the ban in Annex V, point 3? How about if a hotel
delivers food outside the restaurant’s premises?
The packaging ban in Annex V, point 3, applies to the HORECA sector, which should be
understood in line with the definition in Article 3(1), point (35), which in turn refers to NACE Rev.
2. Hotels are included in the HORECA sector, which means that room service falls under the ban.
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However, if a hotel delivers food and beverages in packaging outside their premises, then such
packaging is not banned under Article 25 and Annex V, point 3. However, in that case, the
obligations relating to refill and re-use in the take-away sector, as specified under Articles 32 and
33, apply.
9) Is the list of examples outlined in the ‘illustrative example’ column of Annex V
exhaustive?
The list is not exhaustive, as its wording (‘illustrative example’) demonstrates. The formats that
fall within the scope of the bans will be further explained in the Commission guidelines to be
developed by 12 February 2027, as mentioned in the answers to the previous questions.
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XIII. REUSE AND REFILL
Reusable packaging (Article 11)
1) How will the rotations or trips of reusable packaging be calculated?
Reusable packaging must be designed to ensure a minimum number of rotations, which will be
established in the delegated act to be adopted under Article 11(2). The obligation to calculate and
report on the number of rotations for reusable transport packaging will depend on the type of reuse
system. In particular, open-loop reuse systems without a system operator are exempted from this
obligation (Annex VI, Part A, section 1 (i)). Closed-loop reuse systems with system operators must
report on the number of rotations or trips for each individual reusable packaging, or for an average
estimation if the calculation for each individual reusable packaging is not feasible.
The detailed rules on the calculation of the achievement of the re-use targets contained Article 30
will be clarified in the implementing act to be adopted under Article 12(6). This act will also specify
the situations where it is considered that an individual QR code and tracking of rotations is not
feasible and the calculation of rotations can be made based on an average estimation.
Manufacturers need to demonstrate that the design of reusable packaging and the related system
for reuse allow packaging to comply with the minimum number of rotations requirement. This will
need to be done at the time of placing packaging or a packaged product on the market in the
technical documentation and applies both to reusable packaging circulating in open loop and closed
loop reuse systems.
According to Article 27 and Annex VI, reuse systems must be designed to ensure that reusable
packaging rotating within them completes at least the minimum intended number of rotations as
set out in the delegated act. This will be verified by the Member States’ market surveillance
authorities (Article 62(1), point (h)).
Reuse systems
2) What is an ‘open loop’ reuse system and what are some concrete examples of such
systems?
Open loop reuse systems are characterised by interoperability where reusable packaging can
circulate across different companies, locations, product categories, or sectors rather than being
returned to the single system operator. Open loop reuse systems do not necessarily mean that
reusable packaging becomes the property of the consumer once paid for; this will depend on the
business model. Such reuse systems are normally characterised by using standardised packaging,
shared infrastructure (e.g. for collection, washing and redistribution), and are often coordinated by
a system operator, who manages the logistics and ensures quality, even if the existence of a system
operator is not a legal requirement under the PPWR.
Under the PPWR, open-loop systems without a system operator are exempted from the reuse
labelling requirements and from the reporting on the number of rotations achieved.
Examples of open loop systems without a system operator are the following:
The 0.33-liter longneck reusable bottle system (in Germany): this system is mostly used by
brewers, but also by mineral water companies and other carbonated soft drink producers. Although
there is a standard for the bottle issued by the German Brewers Association and a licensing system
for participants, there is no system operator.
The Euro Pallet: this system has a standard for the pallets, and licensees for production are issued,
but there is no system operator or system management, even though an association (i.e., EPAL) is
responsible for licensing and some other services.
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3) How can economic operators using reusable packaging ensure that a proper reuse
system is in place?
According to Article 27 PPWR, economic operators using reusable packaging must participate in
one or more re-use systems and ensure that these systems comply with the requirements laid down
in the PPWR, Part A of Annex VI. Economic operators also have the possibility to set up their own
re-use system, which must comply with Annex VI. The PPWR establishes the minimum
requirements for the reuse systems in its Annex VI, and the sector needs to find ways to cooperate
and find the most appropriate solutions, depending on their respective products and the local
circumstances, to optimise the functioning of the reuse system.
4) Does a reuse system need to be open for all end users?
Re-use systems can vary in size and geographical coverage and range from smaller local systems
to larger systems that may span over one or several Member States’ territory. Reuse systems do
not have to cover the entire MS. They must however provide equal access and fair conditions to
the end users in the area in which they operate.
Reuse targets for transport packaging
5) Would the exemption for cardboard boxes from the reuse targets for transport
packaging cover interlayers and corrugated cardboard?
Article 29(4)(d) exempts cardboard boxes from the scope of the reuse targets. This should be
understood as including corrugated cardboard boxes. However, the list of exemptions contained in
Article 29(4) must be understood strictly and is limitative, in terms of material, format and use.
Therefore, the exemption of cardboard refers only to cardboard boxes and does not include
interlayers. Nevertheless, since they are also not a format that is explicitly listed in Article 29(1)
and therefore, interlayers are also not concerned by the reuse targets in the first place.
6) What packaging formats are covered by the exemption for flexible formats for
transport packaging?
Article 29(4)(c) excludes from the targets transport packaging flexible packaging formats that are
used for transportation and that are in direct contact with food and feed, as defined in Article 2 and
in Article 3, point (4), of Regulation (EC) No 178/2002 or with food ingredients as defined in
Article 2(2), point (f), of Regulation (EU) No 1169/201.
Therefore, all flexible formats, such as big bags or flexible intermediate bulk containers, as listed
in Article 29(1), which are not used for direct contact with food and feed, and also not used for the
transportation of dangerous goods (exemption envisaged under Article 29(4)(d)), and not custom-
designed for the transportation of large-scale machinery (exemption envisaged under Article
29(4)((b)) should comply with the reuse targets set forth in Article 29(1) to (3).
These will be further specified in the context of the Implementing Act under Article 30 on the rules
on the calculation of the achievement of the re-use targets.
7) Do ‘pallet wrappings and straps’ count as one format or two separate formats?
Pallet wrappings and straps are different packaging formats, but they may be part of the same
transport unit for the purpose of calculating compliance with reuse targets under Article 29. This
will be further clarified in the implementing act under Article 30 on the rules on the calculation of
the achievement of the re-use targets.
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8) If a format is not indicated in Article 29(1), can it still be in the scope of the reuse
targets for transport packaging? Are all flexible packaging formats, such as sealed
bags, in that scope or only those formats listed in paragraph 1?
Article 29(1) lays down an exhaustive list of packaging formats covered by reuse targets, including
their flexible formats. If a sealed bag is an intermediate bulk container, it is within the scope of the
reuse targets, unless it is in direct contact with food and feed, as specified in Article 29(4)(c), in
which case it is exempted.
9) What is the definition of a transport unit?
The term is not defined nor used in the Regulation, but it might be defined in the future for the
purpose of the rules on the calculation of the achievement of the re-use targets in the implementing
act to be adopted under Article 30(3).
Reuse targets for beverages
10) Do the reuse targets for beverages apply to non-alcoholic and alcoholic beverages
individually considered or are they joint targets?
The reuse target for beverages provided for in Article 29(6) applies to both alcoholic and non-
alcoholic beverages. Final distributors, such as retailers, bars and restaurants, can decide what type
of beverages (alcoholic, non-alcoholic or both) they offer for sale to consumers in reusable
packaging in order to fulfil the reuse target. Final distributors shall, however, ensure that beverages
of their own brand contribute on a fair and proportionate basis towards the achievement of the reuse
target.
11) What beverages fall under the scope of the reuse targets for beverages?
The beverages within the scope of the reuse targets for beverages in Article 29(6) will be clarified
in Commission guidelines to be adopted by 12 February 2027. The guidelines will be developed in
consultation with the Member States and other relevant stakeholders.
Article 29(7) specifies that certain beverages are exempted from the reuse targets. This includes:
• Beverages which are highly perishable within the meaning of Article 24 of Regulation
(EU) No 1169/2011 (22).
• Milk and milk products listed in Part XVI of Annex I to Regulation (EU) No 1308/2013 (23)
and their dairy analogies falling within codes 2202 99 11 and 2202 99 15 of the Combined
Nomenclature (CN) in Annex I to Council Regulation (EEC) No 2658/87 (24). Categories
of grapevine products listed in points 1, 3 to 9, 11, 12, 15, 16 and 17 of Part II of Annex
VII to Regulation (EU) No 1308/2013.Aromatised wine products as defined in Regulation
(22) Regulation (EU) No 1169/2011 of the European Parliament and of the Council of 25 October 2011 on
the provision of food information to consumers, amending Regulations (EC) No 1924/2006 and (EC)
No 1925/2006 of the European Parliament and of the Council, and repealing Commission Directive
87/250/EEC, Council Directive 90/496/EEC, Commission Directive 1999/10/EC, Directive 2000/13/EC
of the European Parliament and of the Council, Commission Directives 2002/67/EC and 2008/5/EC and
Commission Regulation (EC) No 608/2004 (OJ L 304 22.11.2011, p. 18)
(23) Regulation (EU) No 1308/2013 of the European Parliament and of the Council of 17 December 2013
establishing a common organisation of the markets in agricultural products and repealing Council
Regulations (EEC) No 922/72, (EEC) No 234/79, (EC) No 1037/2001 and (EC) No 1234/2007 (OJ L
347, 20.12.2013, pp. 671–854)
(24) Regulation (EU) 2018/196 of the European Parliament and of the Council of 7 February 2018 on
additional customs duties on imports of certain products originating in the United States of America
((OJ L 044 16.2.2018, p. 1)
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(EU) No 251/2014 of the European Parliament and of the Council. Products that are similar
to wine products and aromatised wine products and that are obtained from fruit other than
grapes and vegetables, and other fermented beverages falling within CN code 2206 00.
Alcohol-based spirituous beverages corresponding to CN heading 2208.
12) Can Member States set national reuse targets for beverages?
By 2030, Member States shall fulfil the waste prevention targets specified in Article 43(1). Member
States may need to complement the harmonised EU measures with national measures, as specified
in Article 51(2)(c). Member States may increase the harmonised reuse targets set forth in Article
29(6) or set reuse targets for other beverages. This may include beverages that are expressively
exempted under Article 29(7).
To implement national reuse targets, a Member State needs to prove that this is necessary to meet
the waste prevention targets, so as to avoid compromising the objective of market harmonisation.
The targets will need to be notified to the Commission via the TRIS procedure, since such measures
are technical regulations.
Member States can keep existing national reuse obligations in force until 1 January 2030, but from
this date onwards the reuse targets in the PPWR will prevail. For further information on under what
conditions that Member States can set national reuse targets, please consult the Commission
guidance document.
13) Are operators of restaurants or bars covered by the 10% reuse obligation set on
beverages?
All final distributors, including the ones in the HORECA sector, are obliged to fulfil the reuse
targets for beverages provided for in Article 29. However, to minimise burdens on smaller
businesses, final distributors with a sales area of less than 100 m2 are exempted from this obligation
by Article 29(6). Final distributors which make less than 1000 kg of packaging available on the
territory of the Member State per year and fall under the definition of a micro-enterprise, are also
exempted from the reuse target for beverages by Article 29(13)(a).
14) Is single use beverage packaging exempted from the reuse targets for beverages if it
is part of a deposit and return system?
The obligation to fulfil the reuse targets for beverages in Article 29(6) applies to final distributors
such as retailers and restaurants.
The PPWR does not contain a general exemption for single-use beverage packaging in a deposit
and return system, but it provides a large number of exemptions and flexibilities. These includes:
o All final distributors with a sales area under 100 m2 are fully exempted (Article 29(10))
o Member States can exempt final distributors on small islands with less than 2000
habitants (Article 29(11))
o Member States can exempt final distributors if their sales area is located in a
municipality with population density of less than 54 persons/km2. However, the targets
will apply to final distributors with a sales area in population centres with more than
5000 inhabitants (Article 29(11)).
o Member States can allow final distributors to form pools for the purpose of meeting their
reuse obligations jointly. This means that up to 5 final distributors, for example in
densely and remote areas, can share the reuse obligation (Article 29(12)).
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o All final distributors, who are micro-enterprises and do not make more than 1000 kg. of
packaging available in a Member State a year, are fully exempted (Article 29(13))
o Member States can provide further exemptions for final distributors under certain
conditions according to Article 29(14) and specified in point 25 of the Commission
guidance document.
If all exemptions and flexibilities are fully applied in a Member State, the number of final
distributors that are required to fulfil the reuse targets for beverages, will be limited. These final
distributors would enjoy a high degree of flexibility in meeting the targets ensuring that national
circumstances can be taken into consideration.
15) The reuse targets for beverages apply from 2030, which allows time to make the necessary
adjustments to apply to the 10 % target. The Commission will review the reuse targets in
2034 in the light of the experiences gained. Under what circumstances will the
Commission use its empowerment to exempt certain packaging formats or economic
operators from the reuse targets?
The Regulation empowers the Commission to adopt delegated acts supplementing the harmonised
reuse targets for transport packaging, grouped packaging and beverages provided for in Article 29.
Such delegated acts can be adopted under strict legal conditions, and only if it is necessary to take
account of the latest scientific and economic developments.
The empowerment to adopt delegated acts can only be used to exempt economic operators who
face particular economic constraints, or specific packaging formats where achievement of the reuse
targets is hindered due to either hygiene and food safety issues or environmental issues following
the proper impact assessment as specified under the better regulation guidelines (Better regulation:
guidelines and toolbox).
https://commission.europa.eu/law/law-making-process/better-regulation/better-regulation-guidelines-and-toolbox_en
https://commission.europa.eu/law/law-making-process/better-regulation/better-regulation-guidelines-and-toolbox_en
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XIV. PLASTIC CARRIER BAGS
1) Are compostable waste bags considered lightweight plastic carrier bags?
No. Only sales bags (i.e. carrier bags) are covered by the definition of ‘packaging’ in Article 3(1),
point (1), and the definition of ‘plastic carrier bags’ in Article 3(1), point (55).
Waste bags or doggy bags are products, not packaging, and therefore not covered by PPWR.
2) Can a Member State ban all very lightweight plastic carrier bags?
Very lightweight plastic carrier bags that are needed for hygiene purposes or provided as sales
packaging for loose food to prevent food wastages are not banned under Article 25 PPWR. Member
States may nevertheless decide to ban such bags to meet the sustainable reduction target for
lightweight plastic carrier bags under Article 34(1). However, Article 34(2) requires Member
States to consider the environmental impact of bags when they are manufactured, recycled or
disposed of, and their intended use. Any bans (market restrictions) should also be proportionate
and non-discriminatory. Member States must report to the Commission on the consumption of all
very lightweight plastic carrier bags, even those which are excluded from the EU-wide or the
national bans.
3) What are the requirements for compostable plastic carrier bags under the PPWR?
Compostable bags are exempted from the general packaging ban under Article 25, Annex V, point
6, if they are very lightweight plastic carrier bags and needed for hygiene reasons or for loose food
to prevent food wastage.
The use of other very lightweight or lightweight plastic carrier bags is not banned under Article 25
and Annex V but could be subject to national bans, and other marketing restrictions, adopted under
Article 34(2). Member States may also decide that very lightweight plastic carrier bags or
lightweight plastic carrier bags that have not been banned at EU or national level should be
compostable, under the conditions set out Article 9(2)(a).
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XV. ASSESSMENT OF THE CONFORMITY OF PACKAGING
1) From which date will companies have to carry out the conformity assessment
procedure mandated by the PPWR?
In general, the Regulation applies from 12 August 2026 (Article 71). However, certain key
provisions will apply only from the date specified therein. In several cases, the entry into force of
the obligation is linked to the expiry of a certain time after the adoption of the necessary
implementing or delegated acts. This will give stakeholders and Member States sufficient time to
adapt. When a relevant provision does not specify a specific date for its entry into application, the
general application date applies, and companies will thus have to carry out the conformity
assessment procedure by 12 August 2026.
2) Annex VII refers to packaging ‘type’. Does this wording mean the same as ‘types’ in
Annex II, table 1?
The word ‘type’ referred to in Annex VII concerning the conformity assessment procedure is not
the same as the packaging types referred to in Annex II. Annex VII refers to each packaging format
or each packaging batch/series and not to packaging materials, which are used for recyclability
assessment.
3) What is meant by ‘the unique identification of the packaging’ referred to in Annex
VIII? Is the normal product traceability enough?
The Regulation does not define ‘unique identification of the packaging”. This wording, referred to
in Annex VIII, means that the packaging itself needs to be identified in terms of the type, batch, or
serial number.
4) Is it sufficient that a single declaration of conformity is drawn up for packaging or a
packaged product? Or is it required that a dossier of all required declarations of
conformity is drawn up as a single document?
When a packaged product is subject to more than one Union act requiring an EU declaration of
conformity, such as the declaration of compliance under Article 15 of Regulation (EU) 10/2011 on
plastic materials and articles intended to come into contact with food or Article 16 of Regulation
(EC) No 1935/2004 on food contact materials, a single EU declaration of conformity may be drawn
up for all Union acts. That declaration must state the Union acts concerned and their publication
references. It may consist of a dossier of relevant individual EU declarations of conformity.
Therefore, manufacturers have a margin of discretion in assessing the necessity of drawing up a
single declaration of conformity. However, in case a single declaration of conformity is drawn up,
it must clearly distinguish the packaging from the packaged products. The manufacturer may
decide whether the single declaration of conformity is presented as a dossier with different
declarations of conformity or as a single document. If they are presented as a single document, the
conformity assessment for the packaged product and the packaging should still be done and
presented separately.
5) Is the assessment of conformity to be drawn up for each part of the packaging, such
as a bottle, closure and label, or for the entire packaging unit?
The assessment of conformity must be performed, and the declaration of conformity must be drawn
up, for the entire packaging unit. The assessment should include all integrated and separate
components.
6) Is a conformity assessment procedure required for the exemptions set out in Article 6
on recyclability and in Article 7 on recycled content?
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Compliance with the exemptions set out in Article 6 on recyclability and in Article 7 on recycled
content should indeed be assessed and be included as part of the technical documentation referred
to in Annex VII.
7) The wording ‘type, batch or serial number or other element’ in Article 15(5) suggests
that manufacturers can choose to only indicate one of these. Which one?
The wording should be understood as a type, batch or serial number or other element allowing the
identification of the packaging in question. Manufacturers can choose freely among these.
8) Is a manufacturer obliged to contact the competent authorities in each Member State
where its packaging could end up?
There are similar obligations for manufacturers in Article 15(8) and distributors in Article 19(5) to
inform the authorities if they suspect non-compliance in the countries where they have made the
packaging or the packaged product available. The obligation of the manufacturer is to inform the
competent authority in the country or countries where it had made the packaging or packaged
product available on the market for the first time.
In cases where a manufacturer delivers products from one Member State to the warehouse of a
distributor in another Member State, and the latter serves different national markets from the
warehouse, it is the obligation of the distributor to inform the competent authority in each of those
Member States.
9) Can packaging that was placed on the market before the date of application of the
Regulation or of the relevant provisions remain on the market?
In general, packaging which was lawfully placed on the market before 12 August 2026, or
otherwise before the date of application of a specific provision, may remain on the market without
having to be brought into compliance, withdrawn or recalled. As an exception to this rule, for
reusable packaging the cut-off date is 11 February 2025 (Article 15(9) PPWR), which means that
packaging placed on the market before this date can remain on the market without having to be
brought into compliance, withdrawn or recalled.
10) How should a presumption of conformity be construed in relation to the harmonised
EU standards?
The PPWD sets out a number of requirements for placing packaging on the market (essential
requirements). These can be considered as predecessors of the sustainability requirements in the
PPWR. Under the PPWD, compliance with these essential requirements was presumed if
packaging was compliant with the harmonised standards published in the Official Journal of the
European Union (25).
Under the PPWR, the existing harmonised standards can be used only as guidance (see Recital 58),
which means that there can no longer be a presumption of conformity based on these standards.
The only exception to this is laid down in Article 70(1), point (b), in relation to the essential
requirements on packaging minimisation of the PPWD, which applies until end of 2029. This
means that the related harmonised standard can be used for the presumption of conformity until
that date.
(25) EN 13427:2004 ‘Packaging – Requirements for the use of European Standards in the field of packaging
and packaging waste’ EN 13429:2004 ‘Packaging – Reuse’; EN 13430:2004 ‘Packaging – Requirements
for packaging recoverable by material recycling’; EN 13431:2004 ‘Packaging – Requirements for
packaging recoverable in the form of energy recovery, including specification of minimum inferior
calorific value’; EN 13428:2004 ‘Packaging – Requirements specific to manufacturing and
composition – Prevention by source reduction’; EN 13432:2000 ‘Packaging – Requirements for
packaging recoverable by composting and biodegradation’.
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The Commission will consider taking formal measures to repeal the list of the old, harmonised,
standards before the PPWR becomes applicable, to avoid any confusion (26).
Presumption of conformity with new or revised harmonised standards in support of PPWR will
again be possible from the date when a Commission decision listing the relevant harmonised
standards will be published in the Official Journal of the European Union. This publication of
references will allow the presumption of conformity to apply from that date onwards.
11) If a packaging is made from the same materials, but has different sizes, should a
declaration of conformity be drawn up for all sizes of or is just one declaration for all
sizes enough?
According to Annex VII, the manufacturer must draw up a written declaration of conformity for
each packaging type. The declaration of conformity must identify the packaging for which it has
been drawn up. The documentation shall make it possible to assess the packaging’s conformity
with the sustainability requirements, laid down in Article 5 – 12. The technical documentation must
specify the applicable requirements and cover, as far as relevant for the assessment, the design,
manufacture, use and operation of the packaging. For example, the assessment of the minimisation
requirement will depend on the packaged product whereas the assessment of recycled content
might depend on the weight of the packaging.
It follows that the declaration of conformity should be drafted at the level where packaging has the
same characteristics in view of the applicable requirements and the packaged products. Therefore,
if the products differ, a manufacturer should not draft a single declaration of conformity for all
packaging placed on the market.
Concretely, if bottles are of different sizes and contain the same product, and the difference in size
does not affect compliance with any of the requirements in Article 5 – 12, then the manufacturer
may draft a single declaration of conformity for the bottles.
Manufacturers must ensure that the series production of packaging remains in conformity with the
Regulation. They must consider if changes in packaging design or in its characteristics, as well as
changes in harmonised standards or other rules by reference to which conformity is declared or
verified, require reassessment.
12) Does transport packaging also require a conformity assessment and a declaration of
conformity?
There is no exemption for transport packaging. Indeed, completely different packaging types, such
as pallets, pallet collars, wrappings and straps, must undergo separate assessments and must have
separate declarations of conformity.
13) Who will monitor if the recyclability assessment carried out by the manufacturer is
correct?
The manufacturer is obliged to carry out the recyclability performance grade assessment. The result
of this assessment must be included in the technical documentation before the packaging is placed
on the market. Market surveillance authorities will carry out checks based on their national plans
and should apply penalties set at national level in accordance with Article 68.
14) Will economic operators face fines in case they place on the market packaging that is
PPWR-compliant but does not comply with national requirements?
(26) In case of safety legislation with harmonised standards, the harmonised standards cited in the Official
Journal of the European Union under repealed legislation remain valid for the purpose of the
presumption of conformity if these references are not withdrawn from the OJEU. This interpretation
comes from ECJ ruling T-474/15, Global Garden Products vs. Commission.
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To reply to this question, it is necessary to distinguish between:
1) additional national requirements adopted pursuant to Article 4(3) and
2) additional national requirements explicitly allowed in specific articles of the PPWR.
In the case under point 1), fines are not allowed as they have a deterrent effect on the economic
operators and may create market barriers. In the case under point 2), fines are allowed, given that
the Regulation explicitly empowers Member States to go beyond the Regulation. However, such
national fines still must comply with the general rules of the Treaty, in particular proportionality,
which is for Member States to demonstrate. This evidence is to be provided at the time of the TRIS
notification.
45
XVI. WASTE PREVENTION
1) How are the packaging waste reduction targets going to be implemented?
The implementation of packaging waste reduction targets is the responsibility of each Member
State. It is Member States’s responsibility to reach the target and put in place the waste reduction
measures necessary to reach the targets set out in Article 43. While the Regulation harmonises
several packaging waste prevention measures, such as laying down reuse targets, refill and reuse
obligation for take-away sector, packaging bans, and minimisation of packaging requirements,
including empty space thresholds, it is up to the Member States to implement some of these
harmonised measures, as well as to lay down possible additional national waste prevention
measures necessary to reach the targets set out in Article 43(1).
National measures which are applied in addition to the EU harmonised measures may include, but
are not limited to, economic incentives, EPR schemes, and public awareness campaigns, as this is
outlined in Article 43(5). The measures may also include additional obligations on economic
operators, such as higher or additional reuse targets, subject to the conditions under Article 29(15)
and -(16) as explained also in the Commission guidance document. Pursuant to Article 43(5),
national implementing measures must be proportionate and non-discriminatory and be designed to
avoid barriers to trade or distortions of competition. They must not lead to a shift to lighter
packaging material, which does not comply with other sustainability requirements, such as
recyclability, being used to fulfil the goal of the packaging waste reduction.
2) What happens if a Member State does not reach the waste prevention targets?
Each Member State must reduce the packaging waste generated per capita, as compared to the
packaging waste generated per capita in 2018 and as reported to the Commission in accordance
with Decision 2005/270/EC, by at least 5% by 2030, 10% by 2035 and 15% by 2040. The
Commission will monitor the implementation of these targets based on the data on packaging waste
generated reported by Member States. A Member State’s failure to meet the targets is susceptible
to lead to appropriate enforcement action by the Commission.
3) Does the waste reduction target cover all packaging waste generated in a Member
State or only household packaging waste?
The PPWR applies to all packaging and to all packaging waste, whether it originates from industry,
other manufacturing, retail or distribution, offices, services or households. The provisions related
to the calculation of the packaging waste generated (see Article 53(2)) cover all packaging waste
generated on the territory of a Member State. Therefore, the statistical data on packaging waste
generated, as reported by Member States to the Commission, cover all packaging waste generated
on the territory of a Member State.
It is up to Member States to decide how they implement Article 43 and what measures they take to
meet the waste reduction targets established in that provision. Member States can exclude certain
types of waste from the national waste prevention targets and focus merely on the household
packaging waste, if they consider that this will be sufficient to meet the targets. Member States
may maintain the established separate systems for the management of household packaging waste,
on the one hand, and for industrial and commercial packaging waste, on the other hand (Article
43(3)).
4) Will Member States be obliged to notify the national rules they wish to introduce to
achieve the waste reduction targets via the TRIS?
46
Directive (EU) 2015/1535 (27) imposes an obligation on the Member States to notify to the
Commission all draft technical regulations concerning products (and Information Society Services)
before they are adopted in national law.
The term ‘technical regulation’ should be understood broadly. It means technical specifications,
other requirements or rules on Information Society services which are laid down by the Member
States, the observance of which is compulsory, de jure or de facto, for the marketing or use of a
product, for the provision of a service or the establishment of a service operator. It covers also
regulations or administrative provisions prohibiting the manufacture, importation, marketing or use
of a product or prohibiting the provision or use of a service, or establishment as a service provider.
Therefore, all new draft implementing measures, which are technical regulations, must be notified
in the Technical Regulations Information System (TRIS) (28). Member States do not need to re-
notify under the TRIS notification procedure their existing national measures which are compliant
with the Regulation.
Notifications by Member States are made at the draft stage, that is, at a stage of preparation at
which substantial amendments can still be made (Article 1(1)g) of Directive (EU) 2015/1535).
National technical regulations which were not notified can be declared inapplicable to individuals
by the national courts (29).
5) Obligation for the Member States to ensure that their national measures that were
adopted to achieve the packaging waste reduction targets do not ‘lead to a shift to
lighter packaging material being used to fulfil the goal of packaging waste reduction’
and that such measures also ‘reduce the quantity of plastic packaging waste generated’.
This obligation is placed on the Member States, and they must inform on how they achieve this
result in their waste prevention programmes adopted under Article 42(2) PPWR and in the TRIS
notification procedure. The Commission has a general monitoring competence and may also decide
to help Member States by giving additional guidance. However, the Commission does not have a
specific empowerment to provide guidance on the implementation of this provision.
(27) Directive (EU) 2015/1535 of the European Parliament and of the Council of 9 September 2015 laying
down a procedure for the provision of information in the field of technical regulations and of rules on
Information Society services (OJ L 241, 17/09/2015, p. 1–15).
(28) TRIS - European Commission.
(29) ’CIA-Security’ (Case C-194/94).
https://technical-regulation-information-system.ec.europa.eu/en/search
47
XVII. EXTENDED PRODUCER RESPONSIBILITY
1) Are micro-enterprises exempted from Extended producer responsibility (EPR)
obligations?
There is no general exemption for micro-enterprises from EPR obligations in the PPWR or
Directive 2008/98/EC (Waste Framework Directive (WFD)). All producers are responsible for
waste management of the packaging that they make available on the territory of a Member State
for the first time. This includes registering in and reporting to that Member State’s register of
producers according to Article 44.
To minimise administrative burdens on small producers, the PPWR sets fewer reporting obligations
on producers who make less than 10 tonnes a year of packaging available on the market of a
Member State. Furthermore, Member States and producer responsibility organisations (PRO) must
ensure equal treatment of producers regardless of their origin or size and must not place
disproportionate burdens on small producers.
Member States continue to have the right to invoke lower administrative fees for smaller producers
as established in the WFD after the application of PPWR. WFD establishes that were justified by
the need to ensure proper waste management and the economic viability of the extended producer
responsibility scheme, Member States may, provide that:
• in the case of extended producer responsibility schemes established to attain waste management
targets and objectives established under legislative acts of the Union, the producers of products
bear at least 80% of the necessary costs;
• in the case of extended producer responsibility schemes established on or after 4 July 2018 to
attain waste management targets and objectives solely established in Member State legislation,
the producers of products bear at least 80% of the necessary costs;
• in the case of extended producer responsibility schemes established before 4 July 2018 to attain
waste management targets and objectives solely established in Member State legislation, the
producers of products bear at least 50% of the necessary costs;
• and provided that the remaining costs are borne by original waste producers or distributors. This
derogation may not be used to lower the proportion of costs borne by producers of products
under extended producer responsibility schemes established before 4 July 2018.
The PPWR establishes that the producer is either the manufacturer, importer or distributor of
packaging – depending on the context and whether the packaging is transport, sales, grouped,
primary or service packaging. If a manufacturer is a micro-enterprise and that manufacturer is also
the producer of the packaging, it will be exempted from its EPR-requirements when the supplier
of the packaging materials is established in the same Member State.
2) To what extent does the PPWR harmonise national EPR schemes?
The PPWR harmonises certain administrative EPR obligations to lower the administrative burden
for economic operators selling packaging or packaged products in multiple Member States. These
requirements are related to registration, reporting deadlines and frequency, and the granularity of
the data that needs to be reported.
The PPWR also harmonises who the producer is in a Member State. It is the packaging type and
selling technique that determine whether a company is responsible for EPR obligations. Further
information on how the definition of the producer applies, can be found under point II of this
document.
Finally, the PPWR also harmonises the criteria for eco-modulation of EPR-fees. The eco-
modulation will be based on the recyclability performance grades set in Article 6. Member States
48
are allowed to use additional criteria, such as reusability and recycled content, when they apply the
framework for eco-modulation in their national EPR schemes.
In other areas, Member States continue to have a wide flexibility to organize EPR systems and
waste management according to the national conditions and legal settings.
3) Which is the first calendar year that producers must report to the register of
producers?
All Member States shall establish a register of producers that producers must register in and report
to. By February 2026, the Commission shall adopt an implementing act laying down the format for
EPR registering in and reporting to the EPR register (Article 44(14) PPWR). Member States will
have 18 months to establish the register after the adoption of the act (Article 44(1) PPWR).
Producers shall report by June for each full preceding calendar year, and producers will therefore
have to report to the national EPR registers according to the new harmonised rules for the first time
by 1 June 2029.
4) What is the scope of the activities that online platforms can fulfil on behalf of their
sellers?
Based on a written mandate by producers, online platforms can offer to pay the EPR fees in each
Member State where the packaging or packaged products are made available on the market directly
to consumers (Article 45(4) PPWR). However, only the producer, or its PRO or authorised
representative, is responsible for the EPR registration and reporting. An online platform cannot
fulfil these obligations on their behalf unless the producer has chosen to appoint the platform as an
authorised representative.
5) Does an online platform need to check every producer before allowing them to use
the platform?
To prevent free riding as regards EPR obligations, and in line with the obligations in the Digital
Services Act (DSA) (30), the PPWR provides that online platforms that allow consumers to
conclude distance contracts with producers shall obtain information from producers that they are
registered in the EPR register in the Member State where the consumer resides and a self-
certification confirming that their EPR-obligations for packaging are fulfilled.
The online platform shall obtain this information prior to allowing the producers to use the
platform’s services. The online platform shall make best efforts to assess whether the information
provided is reliable and complete, by using or verifying freely available online databases and online
interfaces (Article 45(6) PPWR). This may include requesting the producers to provide supporting
documents (Article 45(8) PPWR). Making best efforts usually requires the verification of the
information provided by the producer with the data in the register of producers.
(30) Regulation (EU) 2022/2065 of the European Parliament and of the Council of 19 October 2022 on a
Single Market For Digital Services and amending Directive 2000/31/EC (OJ L 277, 27.10.2022, pp. 1–
102)
49
XVIII. RETURN AND COLLECTION SYSTEMS
1) How will priority access for recycled materials work in practice?
Collection systems and recycling facilities may provide priority access to recycled materials for
use in applications where the distinct quality of the recycled material is preserved or recovered in
such a way that it can be recycled further and used in the same way and for a similar application
with minimal loss of quantity, quality or function (Article 48(2) PPWR).
The objective of this provision is to help economic operators comply with their recycled content
requirements for plastic packaging under the PPWR. Therefore, Member States may establish such
systems with regards to plastic packaging.
If such systems are established, priority access to the plastic recycled materials should be granted
at market prices. The quantity of recyclates to which priority access is given should correspond to
the quantity of packaging made available on the territory of the Member State by the economic
operator within a specified timeframe. It is Member States who decide to establish such priority
access systems must ensure that these conditions are complied with and monitored and shall notify
such systems via TRIS.
2) What does it mean that packaging is separately collected?
Separate collection is defined in the WFD as ‘the collection where a waste stream is kept separately
by type and nature so as to facilitate a specific treatment’. Member States must ensure that systems
and infrastructure are set up to provide for the separate collection of packaging waste in accordance
with the waste hierarchy, and to facilitate its preparation for re-use and high-quality recycling.
More generally, Member States must ensure that the collection of the packaging materials is
sufficient to achieve the recycling targets laid down in Article 52 and they must establish
mandatory collection objectives for this purpose.
The requirements for separate collection vary. For example, separate collection of single-use
beverage packaging of plastic and aluminium in Article 50 refers to collection in a deposit and
return system.
Calculation and reporting requirements for separate collection for the purpose of complying with
the separate collection requirement under Article 50(1), and for the purpose of establishing the ‘at
scale’ methodology, will be specified in an implementing act to be adopted by 12 February 2027
under Article 56(7).
3) How is composite packaging accounted for in the calculation of recycling targets?
According to Article 53(3), Member States must calculate recycling targets for composite
packaging based on all materials contained in the packaging unit. Pursuant to Article 53(4),
Member States may derogate from this requirement where a given material constitutes an
insignificant part of the packaging unit, and in no case more than 5% of the total mass of the
packaging unit. The 5 % threshold applies to the total mass of the packaging unit.
4) Are the terms ‘ferrous metal’, ‘ferrous metal (including tinplate)’ and ‘steel’ all
synonymous for ‘ferrous metal including tinplate’?
The terms ‘ferrous metal (including tinplate)’ is used in the PPWR only in the context of Member
States’ reporting on reusable packaging. It is also referred in Table 1 of Annex II regarding
materials and formats for which DfR criteria will be established.
In the interest of coherence, the terms ‘steel’ in Table 3 of Annex XII and the term ‘ferrous metals’
used in Article 52(1)(b) and (d), and in Table 1 of Annex XII, also include tinplate.
50
XIX. DEPOSIT AND RETURN SYSTEMS
1) Does the exemption from setting up a deposit and return systems (DRS) apply to the
two beverage packaging types separately?
The 90 % separate collection targets for single-use plastic beverage bottles and metal beverage
containers are two separate collection targets that apply by 1 January 2029. An exemption from the
requirement to be part of a DRS would therefore need to be obtained separately for each format.
Article 50(5) establishes that Member States which collect more than 80% of all single-use plastic
beverage bottles or metal beverage containers within the scope of the PPWR by 2026 may be
exempt from the obligation to set up a DRS. Member States would also have to show with concrete
measures how they will reach 90% separate collection targets by 2029 without setting up a DRS
when notifying the Commission about their request for an exemption.
2) Can a Member State set additional national requirements for DRS?
Pursuant to Article 50(9) PPWR, Member States may adopt provisions for DRS which go beyond
the minimum requirements set forth in Article 50 and in Annex X, while observing the Treaty on
the functioning of the EU and acting in accordance with the PPWR.
For example, Member States are encouraged to establish or maintain DRS for single-use glass
beverage bottles and beverage cartons and may include beverages which are not required to be part
of a DRS under Article 50(4), such as wine, spirits or milk-based products, as well as for other
products. They should, however, be mindful of the negative impact on the internal market of such
rules and should take account of the recommendations in the Communication from the Commission
— Beverage packaging, deposit systems and free movement of goods (2009/C 107/01). Member
States should encourage DRS for reusable packaging, in particular for reusable glass beverage
bottles.
Member States must ensure that the return of packaging is convenient for end users and may
establish additional minimum requirements to ensure that the objectives of the Regulation are met
and to increase the purity of the collected packaging waste and reduce litter (Article 50(9) PPWR).
3) What is to be understood by ‘high transboundary business’ in Annex X?
Annex X requires that Member States with regions with high transboundary business ensure that
the DRS allow for collection of packaging from other Member States’ DRS at designated collection
points and that they must endeavour to enable the possibility of return of a deposit that was charged
to the end user when purchasing the packaging.
Member States will need to assess if this requirement applies when ensuring compliance with the
minimum requirements in Annex X. The minimum requirements apply to DRS established after
11 February 2025, whereas for the existing DRS, Member States must only apply the requirements
from 1 January 2035 if the 90% separate collection targets are not reached by 1 January 2029
(Article 50(11) PPWR). Given that an increasing number of Member States is establishing DRS,
the need for transboundary collaboration between the DRS’ is likely to increase to ensure separate
collection of beverage packaging. The Commission must assess best practice of such measures by
2038 in collaboration with Member States to strengthen interoperability of DRS from different
Member States (Article 50(11) PPWR).
4) Do all DRS have to be non-profit?
A DRS for single-use beverage bottles of plastic and metal containers established after 11 February
2025 must be non-profit, as specified in the minimum criteria set out in Annex X, point f.
51
DRS established before 11 February 2025 are required to be non-profit by 1 January 2035 only if
the Member State does not reach the 90% separate collection targets when they are first reviewed
or at the latest by 1 January 2029 (Article 50(11) PPWR).
5) Is packaging of milk, wine and spirits also exempted from the 90% separate collection
targets?
According to Article 50(4), single-use plastic beverage bottles and metal containers with milk and
milk-products, wine or products similar to wine and spirits are exempted from the requirement to
be part of a DRS. However, such products must be included in the calculation of the separate
collection targets under Article 50(1). Moreover, Member States have flexibility on whether or not
to include the packaging for these products in their DRS.
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