ID 11371 | 19.08.2020
Le sostanze perfluoro alchiliche (PFAS) sono una grande famiglia di migliaia di sostanze chimiche sintetiche ampiamente utilizzate nella società e presenti nell'ambiente.
Contengono tutti legami carbonio-fluoro, che sono uno dei legami chimici più forti nella chimica organica. Ciò significa che resistono al degrado quando vengono utilizzati e anche nell'ambiente. La maggior parte dei PFAS sono inoltre facilmente trasportati nell'ambiente coprendo lunghe distanze lontano dalla fonte del loro rilascio.
È stato osservato frequentemente che i PFAS contaminano le acque sotterranee, le acque superficiali e il suolo. La bonifica dei siti inquinati è tecnicamente difficile e costosa. Se le emissioni continuano, continueranno ad accumularsi nell'ambiente, nell'acqua potabile e nel cibo.
Per- and polyfluoroalkyl substances (PFAS) are a large family of thousands of synthetic chemicals that are widely used throughout society and found in the environment.
They all contain carbon-fluorine bonds, which are one of the strongest chemical bonds in organic chemistry. This means that they resist degradation when used and also in the environment. Most PFAS are also easily transported in the environment covering long distances away from the source of their release.
PFAS have been frequently observed to contaminate groundwater, surface water and soil. Cleaning up polluted sites is technically difficult and costly. If releases continue, they will continue to accumulate in the environment, drinking water and food.
What are PFAS and what are they used for?
PFAS have a wide range of different physical and chemical properties. They can be gases, liquids, or solid high-molecular weight polymers. They are sometimes described as long-chain and short-chain as a way to group PFAS that may behave similarly in the environment. PFAS are also grouped into subgroups in various other ways based on their structure.
PFAS are widely used as they have unique desirable properties. For instance, they are stable under intense heat. Many of them also have surfactant properties and function, e.g., as water and grease repellents.
Some of the major industry sectors using PFAS include aerospace and defence, automotive, aviation, textiles, leather and apparel, construction and household products, electronics, fire-fighting, food processing, and medical articles.
Over the past decades, global manufacturers have started to substitute long-chain PFAS with shorter-chain PFAS or with non-fluorinated substances. This trend has been driven by the fact that the undesired effects of long-chain PFAS on human health and the environment were assessed and recognised first by scientists and authorities around the globe. Short-chain PFAS can also have similar or other properties of concern.
What are the concerns?
All PFAS are highly persistent in the environment. In fact, they are known to persist in the environment longer than any other man-made substance. As a consequence of this persistence, as long as PFAS continue to be released to the environment, humans and other species will be exposed to ever greater concentrations of PFAS. Even if all releases of PFAS would cease tomorrow, they would continue to be present in the environment, and humans, for generations to come.
Their release and mobility in water and air causes contamination to groundwater and drinking water, which is difficult and costly to avoid. Certain PFAS are known to accumulate in the bodies of living things and cause toxic effects. Certain PFAS are toxic for reproduction and can harm the development of foetuses. Several PFAS have been demonstrated to cause cancer. Some PFAS are also suspected of interfering with the human endocrine (hormonal) system, but testing in this area is ongoing.
PFAS are released into the environment from direct and indirect sources, for example, from professional and industrial facilities using PFAS, during use of consumer products (e.g. cosmetics, ski waxes or clothing) and from food contact materials. Humans can be exposed to them every day at home, in their workplace and through the environment, for example, from the food they eat and drinking water.
How are PFAS regulated in the EU?
Globally regulated PFAS
Since 2009, perfluorooctane sulfonic acid and its derivatives (PFOS) have been included in the international Stockholm Convention to eliminate their use. PFOS has already been restricted in the EU for more than 10 years, under the EU’s Persistent Organic Pollutants (POPs) Regulation
In addition, the Stockholm Convention regulates the global elimination of perfluorooctanoic acid (PFOA), its salts and PFOA-related compounds.
Perfluorohexane sulfonic acid (PFHxS), its salts and PFHxS-related compounds are being considered for inclusion in the Stockholm Convention and consequent global elimination.
The manufacture and use of some PFAS are already restricted under REACH.
PFOA and its salts are listed in entry 68 of the restriction list. The entry covers PFOA, its salts and related substances. There is also a draft delegated act by the European Commission amending the POPs Regulation to eliminate the use of the substance. If approved, it will come into force on 4 July 2020, and the restriction entry under REACH will be superseded by the global elimination under the Stockholm Convention.
There is also an ongoing restriction proposal by Germany and Sweden for the following perfluorinated carboxylic acids (C9-14 PFCAs) including their salts and precursors:
perfluorononan-1-oic acid (PFNA);
nonadecafluorodecanoic acid (PFDA);
henicosafluoroundecanoic acid (PFUnDA);
tricosafluorododecanoic acid (PFDoDA);
pentacosafluorotridecanoic acid (PFTrDA); and
heptacosafluorotetradecanoic acid (PFTDA).
ECHA’s scientific committees have provided their opinion on the proposal and support the restriction. This group is also among the substances being considered by the EU as potential candidates for the Stockholm Convention.
Norway has proposed a restriction on perfluorohexane-1-sulphonic acid (PFHxS), its salts and related substances that is currently being discussed in ECHA’s scientific committees. The opinion of the committees is expected in the first half of 2020. This substance group has also been recommended for inclusion to the Stockholm Convention, therefore a global restriction is highly likely in the coming years.
Germany has also submitted a further restriction proposal for undecafluorohexanoic acid (PFHxA), its salts and related substances.
The Netherlands and Germany, with support from Norway, Denmark and Sweden, have shown interest in preparing a restriction proposal to cover a wide range of PFAS uses – in support of the statements made in the Environment Council in December 2019. They are organising a call for evidence to get more information for such a proposal from 11 May until 31 July 2020.
Furthermore, ECHA and the European Commission are currently carrying out several studies related to PFAS used in fire-fighting foams and textiles. This will provide essential information that will be relevant for ongoing or future restriction work.
Substances of very high concern under REACH
A number of other PFAS are on the REACH Candidate List of substances of very high concern (SVHC).
In June 2019 and January 2020, two PFAS groups were identified as SVHCs. The SVHC identification was based on their persistence, mobility and toxicity, which were considered to pose a threat to human health and wildlife when exposed through the environment (including through drinking water). This SVHC identification identified these PFAS as of equivalent concern to carcinogens, mutagens and reprotoxicants (CMRs) and persistent, bioaccumulative and toxic/very persistent and very bioaccumulative (PBTs/vPvBs) chemicals.
These groups are:
2,3,3,3-tetrafluoro-2-(heptafluoropropoxy)propionic acid, its salts and its acyl halides (HFPO-DA), a short-chain PFAS substitute for PFOA in fluoropolymer production, was the first substance added to the Candidate List. Its ammonium salt is commonly known as GenX.
perfluorobutane sulfonic acid (PFBS) and its salts, a replacement of PFOS.
Evaluation of substances under REACH
Several additional PFAS are on the list for evaluation (Community rolling action plan) over the coming years or have already been evaluated. The evaluation aims to clarify initial concerns on the potential risk to human health or the environment that manufacturing or using these substances could pose.
Classification, Labelling and Packaging (CLP) Regulation
A few PFAS already have a harmonised classification and labelling under the CLP Regulation. These include:
perfluorooctanoic acid (PFOA);
ammonium pentadecafluorooctanoate (APFO);
perfluorononan-1-oic acid (PFNA) and its sodium and ammonium salts;
nonadecafluorodecanoic acid (PFDA) and its sodium and ammonium salts.
Perfluoroheptanoic acid has been proposed for harmonised classification and labelling and is in opinion development at the moment.
An informal coordination group of several EU Member States, ECHA and the European Commission has, since 2014, screened data on PFAS contained in ECHA’s registration database and coordinated group-based regulatory work.
Despite an efficient approach compared to regulating substance by substance, work has only been able to cover the PFAS groups of highest urgency due to the very large number of PFAS.
ECHA’s database contains information of over 2 000 individual PFAS on the EU market. These belong to a variety of subgroups and it seems, based on the experience that it would take too long to assess and, where relevant, manage risks subgroup by subgroup. Therefore, ECHA acknowledges that a holistic group approach to the regulatory assessment and risk management needs to be explored, as requested in the proposal for an EU strategy for PFAS, submitted to five Commissioners from several Member States in December 2019.
The provisional agreement by the European Parliament and the Council in December 2019 on the recast of the Drinking Water Directive includes a limit of 0.5 µg/l for all PFAS. This is in line with a grouping approach for all PFAS.
This agreement is now subject to formal approval by the European Parliament and the Council. Following approval, the Directive will be published in the EU's Official Journal and enter into force 20 days later.
PFAS and food
PFAS are released into the environment through industrial manufacturing not directly linked to food production and through the use and disposal of PFAS-containing products. However, as often with persistent pollutants, they end up in the food chain. The main contributors to human dietary exposure are certain vegetables but drinking water is also an important source. Some PFAS also accumulate to human bodies through fish and seafood, meat and meat products, eggs, milk and dairy products.
The European Food Safety Authority (EFSA) is held a public consultation on its draft opinion on PFAS, which ended on 20 April 2020.
68. Acido perfluoroottanoico («PFOA»)
N. CAS 335-67-1
N. CE 206-397-9 e suoi sali.
Qualsiasi sostanza correlata (compresi i suoi sali e polimeri) avente, come uno degli elementi strutturali, un gruppo perfluoroeptil lineare o ramificato con la formula C7F15- direttamente collegato a un altro atomo di carbonio. Qualsiasi sostanza correlata (compresi i suoi sali e polimeri) avente, come uno degli elementi strutturali, un gruppo perfluoroottil lineare o ramificato con la formula C8F17-.
Le seguenti sostanze sono escluse dalla presente denominazione:
- C8F17-X, in cui X = F, Cl, Br.
- C8F17-C(= O)OH, C8F17-C(= O)O-X′ o C8F17-CF2- X′ (in cui X′ = qualsiasi gruppo, compresi i sali)
1. Non deve essere prodotto o immesso sul mercato come sostanza in quanto tale a decorrere dal 4 luglio 2020.
2. A decorrere dal 4 luglio 2020 non deve essere usato per la produzione di o l'immissione sul mercato in:
a) un'altra sostanza, come costituente;
b) una miscela;
c) un articolo in una concentrazione pari o superiore a 25 ppb del PFOA, compresi i suoi sali, o a 1 000 ppb di una sostanza correlata al PFOA o di una combinazione di sostanze correlate al PFOA.
3. I punti 1 e 2 si applicano a decorrere dal:
a) 4 luglio 2022 a:
i) apparecchiature utilizzate per la fabbricazione di semiconduttori;
ii) inchiostri da stampa in lattice;
b) 4 luglio 2023 a:
i) tessuti per la protezione dei lavoratori dai rischi per la loro salute e sicurezza;
ii) membrane destinate all'uso in tessuti medicali, filtraggio nel trattamento delle acque, processi di produzione e trattamento degli effluenti;
iii) nano rivestimenti al plasma;
c) 4 luglio 2032 ai dispositivi medici diversi dai dispositivi medici impiantabili che rientrano nel campo di applicazione della direttiva 93/42/CEE.
4. I punti 1 e 2 non si applicano:
a) all'acido perfluorottansolfonico e ai suoi derivati, che sono elencati nell'allegato I, parte A, del regolamento (CE) n. 850/2004;
b) alla fabbricazione di una sostanza, se questa è un inevitabile sottoprodotto della produzione di composti chimici fluorurati con una catena costituita da un numero di atomi di carbonio pari o inferiore a 6;
c) a una sostanza da usare o che è usata come sostanza intermedia isolata trasportata, purché siano soddisfatte le condizioni di cui all'articolo 18, paragrafo 4, lettere da a) a f), di tale regolamento;
d) a una sostanza, a un costituente di un'altra sostanza o miscela da usare o che è usata:
i) nella produzione di dispositivi medici impiantabili che rientrano nel campo di applicazione della direttiva 93/42/CEE;
ii) nei rivestimenti fotografici applicati a pellicole, carta o lastre di stampa;
iii) nei processi fotolitografici per i semiconduttori o nei processi di incisione per i semiconduttori composti;
e) alle miscele concentrate di schiume antincendio immesse sul mercato prima del 4 luglio 2020 da usare o che sono usate nella produzione di altre miscele di schiume antincendio.
5. Il punto 2, lettera b), non si applica alle miscele di schiume antincendio che sono state:
a) immesse sul mercato prima del 4 luglio 2020; o
b) prodotte in conformità al punto 4, lettera e), a condizione che, se sono usate a fini di formazione, le emissioni nell'ambiente siano ridotte al minimo e gli effluenti raccolti siano smaltiti in modo sicuro. 6.
Il punto 2, lettera c), non si applica:
a) agli articoli immessi sul mercato prima del 4 luglio 2020;
b) ai dispositivi medici impiantabili fabbricati in conformità al punto 4, lettera d), punto i);
c) agli articoli rivestiti con i rivestimenti fotografici di cui al punto 4, lettera d), punto ii); d) ai semiconduttori o ai semiconduttori composti di cui al punto 4, lettera d), punto iii).
Allegato I, parte A
Acido perfluorottano sulfonato e ai suoi derivati (PFOS)
Allegato I, parte A
Con il Regolamento delegato (UE) 2020/784 della Commissione dell'8 aprile 2020 è stato modificato l'allegato I del Regolamento (UE) 2019/1021 del Parlamento europeo e del Consiglio per quanto riguarda l'elenco di acido perfluoroottanoico (PFOA), suoi sali e composti correlati al PFOA.
Con il Regolamento delegato (UE) 2020/1203 del 9 giugno 2020 è stato modificato l’allegato I del regolamento (UE) 2019/1021 del Parlamento europeo e del Consiglio per quanto riguarda la voce relativa all’acido perfluorottano sulfonato e suoi derivati (PFOS).
segue in allegato
Regolamento (CE) 1272/2008 CLP
Regolamento (CE) N. 1907/2006 REACH
Regolamento (UE) 2019/1021
Regolamento delegato (UE) 2020/1203
Regolamento delegato (UE) 2020/784
Certifico Srl - IT | Rev. 0.0 2020
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