(1)

Regulation (EU) 2019/1009 lays down rules on the making available on the market of EU fertilising products. EU fertilising products contain component materials of one or more of the categories listed in Annex II to that Regulation.

(2)

In accordance with Article 42(1) of Regulation (EU) 2019/1009, the Commission is empowered to adopt delegated acts in accordance with Article 44 for the purpose of adapting Annex II to technical progress.. Pursuant to Article 42(3) of Regulation (EU) 2019/1009 read in conjunction with Article 6 of Directive 2008/98/EC of the European Parliament and of the Council (2), the Commission may include in the component material categories materials that cease to be waste following a recovery operation if such materials are to be used for specific purposes, have an existing market or demand and their use do not lead to overall adverse environmental or human health impacts.

(3)

The Commission’s Joint Research Centre (‘JRC’) has identified certain high purity materials which could be recovered from waste and used as component materials in EU fertilising products (3).

(4)

The high purity materials identified by the JRC are ammonium salts, sulphate salts, phosphate salts, elemental sulphur, calcium carbonate and calcium oxide. All those materials are covered by Regulation (EC) No 2003/2003 of the European Parliament and of the Council (4), have a significant market demand and have proven their high agronomic value during a long history of use in the field.

(5)

As a first measure to ensure both safety and agronomic efficiency, a minimum purity requirement of high purity materials should be laid down. According to the information available in JRC’s assessment report, a 95 % purity, expressed in terms of the dry matter of the material, will ensure high agronomic efficiency with low risks to the environment, health and safety. While, for some materials, this high purity is set at more ambitious levels than those required by Regulation (EC) No 2003/2003, it is estimated that such a higher purity is achievable based on existing practices.

(6)

In addition, it is appropriate to specify that high purity materials are recovered from waste following two types of processes: processes that isolate salts or other elements through (a combination of) advanced purification methods, such as crystallisation, centrifugation or liquid-liquid extraction, often applied in (petro-)chemical industries; and gas purification or emission control processes designed to remove nutrients from off-gases.

(7)

Therefore, the content of certain impurities, pathogens or contaminants which are specific to those materials, or the content of organic carbon should be limited, based on the JRC assessment report. Such criteria should apply in addition to the safety criteria laid down in Annex I to Regulation (EU) 2019/1009 for the corresponding product function category and without prejudice to Regulation (EU) 2019/1021 of the European Parliament and of the Council (5).

(8)

Consequently, additional limit values should be laid down for the contaminants total chromium and thallium. Some of the high purity materials may contain such contaminants as a result of the input materials and the processes they are obtained from. The proposed limit values for those contaminants should ensure that the use of EU fertilising products containing high purity materials with such contaminants does not lead to their accumulation in soil. In addition, requirements on the content of pathogens should be introduced for all EU fertilising products containing or consisting of high purity materials given the broad variety of processes they could be obtained from and the waste streams allowed as input materials. The limit values for both the contaminants and the pathogens should be determined as concentration in the final product, similar to the requirements set out in Annex I to Regulation (EU) 2019/1009. This is justified by the fact that the safety criteria introduced in reply to any particular risks identified concern, as a rule, the final product and not a component material. This should also facilitate the market surveillance of such products, as tests are to be carried out only on the final product.

(9)

Furthermore, additional safety criteria should be laid down to limit the content of 16 polycyclic aromatic hydrocarbons (PAH16) (6) and of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/PCDF) (7). Regulation (EU) 2019/1021 lays down release reductions for PAH16 and PCDD/PCDF as unintentionally produced substances during manufacturing processes, but does not introduce a limit value in such cases. Given the high risks generated by the presence of such pollutants in fertilising products, it is considered appropriate to introduce more stringent requirements than those laid down in that Regulation. Such limit values should be laid down at component material level and not as concentration in the final product, to ensure coherence with Regulation (EU) 2019/1021.

(10)

These limit values may not be relevant for all high purity materials to be included as a new component material category. Therefore, manufacturers should have the possibility to presume the conformity of the fertilising product with a given requirement without verification, such as testing, whenever the compliance with the said requirement follows certainly and uncontestably from the nature or the recovery process of the respective high purity material or of the manufacturing process of the EU fertilising product.

(11)

As an additional safety measure, the high purity materials should be registered based on Regulation (EC) No 1907/2006 of the European Parliament and of the Council (8), in the extensive conditions already laid down in Regulation (EU) 2019/1009 for chemical substances in other component material categories. This should ensure that the manufacturers take into account the use as a fertilising product when performing the risk assessment under that Regulation and that the registration is done also for low tonnage materials.

(12)

Furthermore, some of the high purity materials may be available on local markets in quantities that exceed demand. To ensure that market demand for high purity materials exists and that their long-term storage under suboptimal conditions does not lead to adverse environmental impacts, it is appropriate to limit the period of time during which they can be used as component materials for EU fertilising products after they have been generated. Manufacturers should be required to sign the EU declaration of conformity for the EU fertilising product containing the said material within that period.

(13)

Based on the above, the Commission concludes that high purity materials if recovered following the recovery rules suggested in JRC’s assessment report, ensure agronomic efficiency within the meaning of Article 42(1), first subparagraph, point (b)(ii), of Regulation (EU) 2019/1009. Furthermore, they comply with the criteria laid down in Article 6 of Directive 2008/98/EC. Finally, if compliant with the other requirements in Regulation (EU) 2019/1009 in general and in Annex I to that Regulation in particular, they would not present a risk to human, animal or plant health, to safety or to the environment within the meaning of Article 42(1), first subparagraph, point (b)(i), of Regulation (EU) 2019/1009. Such materials would also have a useful purpose as they would replace other raw materials used in the production of EU fertilising products. Therefore, recovered high purity materials should be included in Annex II to Regulation (EU) 2019/1009.

(14)

Furthermore, given the fact that high purity materials are recovered waste within the meaning of Directive 2008/98/EC, they should be excluded from component material categories 1 and 11 of Annex II to Regulation (EU) 2019/1009 pursuant to Article 42(1), third subparagraph, of that Regulation.

(15)

Some of the high purity materials may contain selenium which can be toxic if present in high concentration. Some may also contain chloride, which may raise concerns regarding the salinity in soil. Whenever those substances are present in concentrations exceeding a certain limit, their content should be indicated on the label so that the users of the fertilising product are properly informed. Annex III to Regulation (EU) 2019/1009 should be amended accordingly.

(16)

It is important to ensure that when fertilising products contain high purity materials, they are subject to an appropriate conformity assessment procedure including a quality system assessed and approved by a notified body. Therefore, it is necessary to amend Annex IV to Regulation (EU) 2019/1009 to provide for a conformity assessment appropriate for such fertilising products.

(17)

Given that the requirements set out in Annexes II and III to Regulation (EU) 2019/1009 and the conformity assessment procedures set out in Annex IV to that Regulation are to apply as of 16 July 2022, it is necessary to defer the application of this Regulation to the same date,

(1)

Annex II is amended in accordance with Annex I to this Regulation;

(2)

Annex III is amended in accordance with Annex II to this Regulation;

(3)

Annex IV is amended in accordance with Annex III to this Regulation.