1 Open Public Consultation Results
1.3 Detailed analysis
1.3.22 Question 26: Please indicate any incoherence (gaps or missing links, overlaps,
which are under the scope of this fitness check
1.3.22.1 Analysis of open text responses
There was no closed element to this question. Respondents were also asked to focus on aspects related to hazard identification, risk assessment and risk management of chemicals. In total, 39 comments in relation to gaps and missing links, 39 comments related to overlaps and 41 comments on inconsistencies were reviewed.
The samples for Question 26 were taken for each of the text boxes on gaps, overlaps, and inconsistencies, thus there are around three times as many comments that have been reviewed as for the other questions. This ensures that equal weight is given to responses on each of the possible types of incoherence. Some comments covered overlaps or inconsistencies in the box for gaps, overlaps in the box for inconsistencies, etc. Therefore, the results for Question 26 have been presented together rather than providing a separate analysis on gaps, overlaps and inconsistencies for each text box. This ensures a more comprehensive assessment across all sampled responses.
The key themes from these comments have been extracted and are summarised in Table 1-64. The table also shows which groups the comments were from.
Table 1-64: Q26: incoherence between different pieces of legislation under the scope of the fitness check themes from non-questionnaire responses (Gaps: n=39; Group 1 (citizens) = 5, Group 2 (industry) = 20, Group 3 (public authority) = 6, Group 4 (NGO/others) = 8; Overlaps: n=39; Group 1 = 5, Group 2 = 22, Group 3 = 6, Group 4 = 6; Inconsistencies: n=41; Group 1 = 4, Group 2 = 24, Group 3 = 6, Group 4 = 7)
Theme By
Themes on gaps and omissions
Too little account of new risks Group 1 (citizen)
Maximum residue limits between pesticides and biocides Group 3 (public authority) Better transfer of information on hazardous substances to the waste section Group 3 (public authority) Clear definition of criteria for endocrine disruptors Group 3 (public authority)
Group 4 (NGO/others) Gaps in and between specific legislation (no details given) Group 2 (industry)
Food contact materials Group 2 (industry)
Group 4 (NGO/others) Cosmetics Products Regulation outlines specific safety assessment procedures
that cannot always be found in other legislation Group 2 (industry)
CLP packaging requirements Group 2 (industry)
Classification of mixtures Group 2 (industry)
Group 4 (NGO/others) Additional steps needed in risk management of active substances for biocides
to allow for cost-benefit analysis Group 2 (industry)
Carcinogens and Mutagens Directive does not cover substances toxic for Group 2 (industry)
Table 1-64: Q26: incoherence between different pieces of legislation under the scope of the fitness check themes from non-questionnaire responses (Gaps: n=39; Group 1 (citizens) = 5, Group 2 (industry) = 20, Group 3 (public authority) = 6, Group 4 (NGO/others) = 8; Overlaps: n=39; Group 1 = 5, Group 2 = 22, Group 3 = 6, Group 4 = 6; Inconsistencies: n=41; Group 1 = 4, Group 2 = 24, Group 3 = 6, Group 4 = 7)
Theme By
reproduction Group 4 (NGO/others)
Gaps in communication along the supply chain Group 2 (industry) Missing connections relating to hazard characteristics and those relating to risk
assessment Group 2 (industry)
Gaps for specific substances Group 4 (NGO/others)
Gap concerning evaluation and reporting on chemicals in low volumes Group 4 (NGO/others) Gap in chemical regulations and content information to consumers for the
majority of consumer goods Group 4 (NGO/others)
Exposure of consumers to hazardous chemicals in imported articles and goods
is not adequately addressed Group 4 (NGO/others)
No clear limit value on content of chemicals in medical devices Group 4 (NGO/others) Setting standards for emission of pollutants in indoor air Group 4 (NGO/others) Drinking Water Directive needs to be enhanced to improve chemical safety of
water supply materials Group 4 (NGO/others)
Themes on overlaps and duplications
Unclear boundaries between IED1 and Urban Waste Water Directive and Water
Framework Directive need to be addressed Group 3 (public authority)
Same substances could be notified and/or evaluated under different legislative
frameworks Group 2 (industry)
PPP2 requires full risk assessment but this can be overridden by classification if
the risk assessment indicates safe use Group 1 (citizen)
Overlaps between directives/regulations (but no details given)
Group 1 (citizen)
Group 3 (public authority) Group 2 (industry) Group 4 (NGO/others) PG2 and 5 overlap with well-functioning and implemented national regulation
and laws Group 1 (citizen)
Same chemicals can be covered by CLP, biocides and plant protection products regulations and different outcomes can be reached even with the same dataset
Group 3 (public authority) RoHS3 and toys directive have same substances regulated Group 3 (public authority) Double regulation of dioxins/furans in POP4 regulation and national
ChemVerbotsV Group 3 (public authority)
Classification and labelling requirement has unduly become reference for
waste classification Group 2 (industry)
Substances on the candidate list and POP regulation Group 2 (industry) RoHS and REACH have substance related overlaps Group 2 (industry) Some instances of double regulation due to legislative changes or guidance Group 4 (NGO/others) Themes on inconsistencies and conflicts
Preventing hazardous substances getting into materials and products Group 3 (public authority)
Use of SVHC5 is hindering recycling Group 3 (public authority)
Different approaches at national level to nanomaterials Group 2 (industry) Group 3 (public authority)
Table 1-64: Q26: incoherence between different pieces of legislation under the scope of the fitness check themes from non-questionnaire responses (Gaps: n=39; Group 1 (citizens) = 5, Group 2 (industry) = 20, Group 3 (public authority) = 6, Group 4 (NGO/others) = 8; Overlaps: n=39; Group 1 = 5, Group 2 = 22, Group 3 = 6, Group 4 = 6; Inconsistencies: n=41; Group 1 = 4, Group 2 = 24, Group 3 = 6, Group 4 = 7)
Theme By
Tighter hazard categories in Seveso Directive from CLP will result in more
substances falling under Seveso requirements Group 2 (industry) Classification can be very different for one product for human use Group 2 (industry) CLP values are not suitable to set safe rules for chemical use in toys Group 4 (NGO/others)
Substance restrictions with different rules Group 2 (industry)
Changes in CLP environmental classification automatically triggers
requirements under Seveso III and there is no assessment as to whether these requirements are appropriate in risk management terms
Group 2 (industry)
Incorrect application of Article 15 of Cosmetics Products Regulation creates an overlap with CLP which leads to inconsistency
Group 2 (industry) Risk assessment used in some cases risk management by hazard identification
in Group 4
Group 1 (citizen) Group 2 (industry) Directives should be united in regulations and directly implemented at national
level Group 1 (citizen)
Inconsistencies between regulations/directives (no further details given)
Group 1 (citizen)
Group 3 (public authority) Group 2 (industry) Controls on biocides and plant protection products are more restrictive than
on general chemicals due to classification based exclusion criteria Group 3 (public authority) Harmonised definition of nanomaterials is needed Group 3 (public authority)
Group 4 (NGO/others) Ban on animal testing for cosmetics but biocides regulation specifically asks for
animal testing Group 3 (public authority)
Issue of animal testing in cosmetics regulation versus other regulations Group 2 (industry) PBT6 assessment is not consistent within different parts of the legislation Group 3 (public authority) Difference in classification of substances between transport and supply and
use Group 3 (public authority)
Divergence between commitment to weight-of-evidence considerations and
how substances are identified as PBT/vPvB7 Group 2 (industry)
Different migration limits for same chemicals for different FCM8 Group 2 (industry) The influence of individual views of Member States Group 2 (industry) CLP has led to unpredicted burden for waste management Group 2 (industry) Waste legislation might be inconsistent with REACH for recycling purposes Group 2 (industry)
OELs9 vary from country to country Group 2 (industry)
Glass is a substance and should not be subject to RoHS Group 2 (industry) Risk assessment principles differ in Toy Safety Directive and Cosmetics Product
Regulation with regard to treatment of children Group 2 (industry) There are inconsistencies between labelling of substances under CLP and some
sectoral legislation (biocides, detergents) Group 2 (industry)
Inconsistency of restrictions in POP regulation Group 2 (industry) Regulation on marketing and use of explosives is inconsistent with statistical
and physical measurement bases Group 2 (industry)
Not all inconsistencies between different legislation are negative Group 4 (NGO/others)
Table 1-64: Q26: incoherence between different pieces of legislation under the scope of the fitness check themes from non-questionnaire responses (Gaps: n=39; Group 1 (citizens) = 5, Group 2 (industry) = 20, Group 3 (public authority) = 6, Group 4 (NGO/others) = 8; Overlaps: n=39; Group 1 = 5, Group 2 = 22, Group 3 = 6, Group 4 = 6; Inconsistencies: n=41; Group 1 = 4, Group 2 = 24, Group 3 = 6, Group 4 = 7)
Theme By
Lists of substances in different pieces of legislation should be harmonised Group 4 (NGO/others) CLP has no de minimis exemption unlike Dangerous Goods directive Group 4 (NGO/others) Themes on labelling
Labelling requirements under different pieces of legislation need to be better
integrated to facilitate compliance Group 2 (industry)
Inconsistent labelling requirements Group 2 (industry)
Detergents Regulation has its own labelling requirements beyond what is required according to CLP
Group 3 (public authority) Group 2 (industry) CLP and plant protection regulation/biocidal products have different
requirements for advertising and labelling Group 3 (public authority) Labelling requirements in transport of dangerous goods, in CLP and in national
authorities requirements Group 2 (industry)
Labelling under BPR10 and CLP for treated articles Group 2 (industry) Classification and labelling differs between ADR11 and CLP Group 2 (industry) Themes on coordination with other legislation
Automatic legal consequences in downstream legislation should be avoided Group 2 (industry) Need for visual mapping and overview of broader architecture and vertical and
horizontal linkages between different legislation Group 2 (industry) Derogation of glass under RoHS should not be reopened by REACH
authorisation process Group 2 (industry)
When a substance is restricted in regulation X, this should trigger a restriction
in regulation Y, Z and evaluation in regulation A, B, C Group 4 (NGO/others) Themes on definitions
Coherent definitions of hazardous substances Group 3 (public authority) Group 2 (industry)
There is not always a common definition Group 2 (industry)
Other themes
Risk assessment should be studied by a laboratory independent of the
manufacturer Group 1 (citizen)
Set of shared references Group 1 (citizen)
Product bans Group 1 (citizen)
Risk assessment issues Group 3 (public authority)
Ignorance of users Group 2 (industry)
Not all substances in Seveso are capable of uncontrolled or spontaneous
release of energy or matter* Group 2 (industry)
Chemical producers should not undertake the evaluation of risks Group 1 (citizen)
Notes: *This is not considered an inconsistency, as Seveso intentionally includes substances that can initiate or aggravate the effects of a major accident.
1 IED = Industrial Emissions Directive. 2 PPP = Plant Protection Product. 3 RoHS = Restriction of Hazardous Substances Directive. 4 POP = Persistent Organic Pollutant. 5 SVHC = Substances of Very High Concern. 6 PBT
= Persistant, Bioaccumulative, Toxic. 7 vPvB = very Persistent very Bioaccumulative. 8 FCM = Food Contact Materials. 9 OEL = Occupational Exposure Limit. 10 BPR = Biocidal Products Regulation. 11 ADR = European Agreement concerning the International Carriage of Dangerous Goods by Road
1.3.22.2 Themes from analysis of sample of non-questionnaire responses
As well as the responses from the OPC, an analysis was made of the themes from nine other responses that were received. Table 1-65 provides a summary of the themes from these non-questionnaire responses.
Table 1-65: Q26: incoherence between different pieces of legislation under the scope of the fitness check themes from non-questionnaire responses (n=9)
Theme By
Themes on gaps and omissions
There is a gap in the requirements for toys Group 3 (public authority) Additional steps in risk management of active substances are needed for
biocides Group 2 (industry)
There is no provision within Regulation EC 396/2005 to enable MRLs1 to be set
for BPR2 product Group 3 (public authority)
Gaps, overlaps, confusions and contradictions creep into the text during
negotiations which are not intended Group 3 (public authority)
Themes on overlaps and duplications
The same substance must be assessed for both PPP3 and BP Regulations Group 3 (public authority) Hazard assessment of the same substances under both Regulation (EC) no
1107/2009) and Regulation (EU) no 528/2012 should be avoided Group 3 (public authority) Article 69(1) BPR (Regulation EU no 528/2012) refers to the provisions of CLP,
including requirements to have labels in the national languages (art. 17(2) CLP). The same issue is dealt with in art. 69(3) BPR
Group 3 (public authority) The Detergents Regulation has its own additional labelling requirements
beyond what is required according to CLP Group 3 (public authority)
The demands are unnecessary since CLP entered into force and it could be
removed Group 3 (public authority)
Both CLP and the Plant Protection Products Regulation/Biocidal Products
Regulation have rules regarding for example advertising and labelling Group 3 (public authority) The RoHS4 Directive and the Toys directive have the same substances
regulated Group 3 (public authority)
Creosote between BPR and REACH Group 3 (public authority)
The large number of separate directives for specific issues e.g. toys, adds to the
complexity Group 3 (public authority)
The parallel existence of hazard reviews under the CLP, BPR and PPP schemes
can prove to be very ineffective and impacting resources Group 2 (industry) None of the three legal texts (CLP, Biocides, and REACH Regulations) foresee a
timely sequence or practical code of work to maximise the use of generated data and the efficiency of the overall classification process
Group 2 (industry) Neither do methodologies documented under one benefit the other. Group 2 (industry) This may result in classifications decided on the basis of incomplete or
non-fit-for-purpose datasets Group 2 (industry)
The hazard assessment for BPR, PPPR and REACH and CLP leads often to
double or multiple work Group 2 (industry)
We should move from an ad hoc system in which classification proposals are submitted under different umbrellas (e.g. Biocides, CLP, etc.), to a more systematic and integrated system.
Group 2 (industry) Article safety legislation is far from harmonised and streamlined Group 2 (industry) Themes on inconsistencies and conflicts
The derogation for medical devices which are invasive in CLP is not written in
the same way as in REACH Group 3 (public authority)
Table 1-65: Q26: incoherence between different pieces of legislation under the scope of the fitness check themes from non-questionnaire responses (n=9)
Theme By
The properties of PFAS5 do not fit in the criteria laid down by REACH Annex
XVIII Group 3 (public authority)
There is a divergence between the commitment to weight-of-evidence
considerations and how substances are being identified as PBTs6/vPvBs7 Group 2 (industry) When it comes to PBT/vPvB criteria the consequences of fulfilling the criteria
are very different. For REACH no immediate consequences; for PPP non-authorisation. The difference in consequences leads to differences in interpretation
Group 3 (public authority)
Regulatory efforts and costs varies significantly between different legislations Group 3 (public authority) The whole REACH system became utterly complex with all the different
substances ‘statuses’ Group 2 (industry)
This could be simplified to a great extent by focussing on the potential for and
pathway of exposure Group 2 (industry)
Themes on labelling
Labelling requirements could be better integrated Group 2 (industry) Labelling requirements under BPR and CLP are sometimes contradictory Group 2 (industry) In the BPR the risks from products might be the same but the extent to which
they are regulated depends upon the claims made on the label Group 3 (public authority) Themes on coordination with other legislation
Monitoring data from other legislation would be useful (e.g. WFD8) Group 3 (public authority) Need to highlight issues for other legislation where water bodies do not fulfil
criteria of WFD Group 3 (public authority)
Needs to be more coordination between WFD and other legislation Group 3 (public authority) REACH datasets are often disregarded in Member State and EU policies, such
as the Water Framework Directive, IED and OSH9 where they are not yet fully recognised as reliable references
Group 2 (industry) Better integration is needed with EU rules on chemicals, articles and waste Group 3 (public authority) It is not possible for EU-authorities to get data on the use of ingredients in
cosmetics Group 3 (public authority)
Themes on definitions
The term “ingredients” is not defined in CLP leading to unclear legal text Group 3 (public authority) Article 1(5) CLP is not clear with regard to the scope of the exemption from CLP Group 3 (public authority) Reg (EC) no 1107/2009 and Reg (EC) no 1272/2008 are vague as to the
designating responsibility to produce classification dossiers Group 3 (public authority) Same definitions can mean different things in different legislations Group 3 (public authority) Better to have rules that impose the same restrictions on all items Group 3 (public authority) Other themes
Automatic legal consequences to more substances falling under Seveso
requirements should be avoided Group 2 (industry)
Evaluation process for active substances in PPP and CLH10 process need to be
re-examined Group 3 (public authority)
The approach indicated by the legislator for 'cut off criteria' is not followed in
practise. Group 3 (public authority)
It is not clear that the legislation leads to substances that stay on the market
are safer than the ones that are removed Group 3 (public authority)
Somewhat unclear or illogical structure of the chemicals legislation in EU
particularly in relation to the legislation concerning substances and mixtures in Group 3 (public authority)
Table 1-65: Q26: incoherence between different pieces of legislation under the scope of the fitness check themes from non-questionnaire responses (n=9)
Theme By
articles (products)
Make better use of self-classifications and to discuss at expert panel level or a broader/more integrated and dynamic group, only self-classifications deviating from the classification rules
Group 2 (industry) Mutual recognition of legislation on food contact materials is not working
effectively Group 2 (industry)
Limit values in different legislations are potentially overlapping and incoherent Group 3 (public authority) Notes: 1 MRL = Maximum Residue Limit. 2 BPR = Biocidal Products Regulation. 3 PPP = Plant Protection Product. 4 RoHS = Restriction of Hazardous Substances Directive. 5 PFAS = Perfluorinated alkylated substances. 6 PBT = Persistant, Bioaccumulative, Toxic. 7 vPvB = very Persistent very Bioaccumulative. 8 WFD = Water Framework Directive. 9 OSH = Occupational Safety and Health. 10 CLH = Harmonised Classification and Labelling
1.3.22.3 Comparison of themes
The themes associated with the incoherence between different pieces of legislation are summarised in the table below. Here the themes focus on the regulations and directives where gaps, overlaps and inconsistencies have been identified. Not all comments provide further details as to what the gap is, where the overlaps are or why there are inconsistencies. Those regulations and directives listed in Table 1-66 that were not included as themes in Tables 1-64 and 1-65 are where no further detail has been provided. Therefore, the table provides a summary of the types of issues identified and the number of times each was reported. Note the count is the number of comments that were attributed to each theme, not the number of respondents. This means one respondent could be counted more than once in the sample if, for example, they made comments that were used in two or more themes. Further details on the gaps, overlaps and inconsistencies are set out below the table, where these were provided by respondents.
Table 1-66: Comparison of responses on incoherence between different pieces of legislation under the scope of the fitness check
Non-questionnaire responses OPC responses
Regulation/directive(s) By Regulation/directive(s) By
Regulations and directives where gaps were identified
Toys Group 3 (1) Cosmetic Products
Regulation and other legislation
Group 2 (1)
Biocides Group 3 (1) CLP packaging
requirements
Group 2 (1) Carcinogen and
Mutagens Directive
Group 2 (1) Group 4 (1) Regulations and directives where overlaps were identified
PPPR1 and BPR2 Group 3 (2) Biocides and pesticides Group 4 (1)
BPR and CLP Group 3 (1) CLP and BPR Group 1 (1)
Group 4 (1) BPR and REACH
(creosote)
Group 3 (1) PPPR, BPR and CLP Group 3 (1)
Group 2 (1)
CLP, biocides, PPPR Group 3 (1) CLP, biocides and REACH Group 2 (1)
Table 1-66: Comparison of responses on incoherence between different pieces of legislation under the scope of the fitness check
Non-questionnaire responses OPC responses
Regulation/directive(s) By Regulation/directive(s) By
PPPR, BPR, CLP and
exposure values (DNEL7, OEL8, European and Regulations and directives where inconsistencies and conflicts were identified
Medical devices, CLP and Cosmetic Products Group 2 (2)
Table 1-66: Comparison of responses on incoherence between different pieces of legislation under the scope of the fitness check
Non-questionnaire responses OPC responses
Regulation/directive(s) By Regulation/directive(s) By
Regulation and CLP CLP and transport regulations
Group 2 (1) Drinking Water Directive,
BPR
Group 1 (1) Contaminants in food,
MSFD9, IED
Group 3 (1) CAD10 and CMD11 Group 2 (1)
RoHS Group 2 (1)
National legislation versus EU legislation
Group 2 (1)
Key: Group 4 captures non-governmental organisation (NGO), consumer association, trade association, trade union, academia or a research or educational institute, other from Question 5 of the OPC.
Notes: 1 BPR = Biocidal Products Regulation. 2 PPPR = Plant Protection Products Regulation. 3 RoHS = Restriction of Hazardous Substances Directive. 4 ELV = End of Life Vehicles Directive. 5 IED = Industrial Emissions Directive. 6 POP = Persistent Organic Pollutant. 7 DNEL = Derived No Effect Level. 8 OEL = Occupational Exposure Limit. 9 MSFD = Marine Strategy Framework Directive. 10 CAD = Chemical Agents Directive. 11 CMD = Carcinogens and Mutagens Directive.
Some of the comments provided just a short summary of the issue without providing any further information. Others, though, provided a detailed discussion of the problem. Examples of key points are provided below:
Comments on gaps and omissions:
o While we agree it can be useful to look for current gaps and missing links in current legislation, we hold the view that not all inconsistencies are bad by definition. There can be good reasons to adapt rules to specific chemical uses or intrinsic hazardous properties. For example, the use of generic risk assessments to phase out chemicals with the most harmful properties from applications with clear exposure of people, including children (Group 3);
o Need to speed up the process of including restrictions for use of certain chemicals in packaging materials, batteries and vehicles in line with the new information on hazards and risks that is generated e.g. under REACH. We propose that a review process should be included in these directives to regularly evaluate the existing limit values and assess the need for including additional substances in the directives
o Need to speed up the process of including restrictions for use of certain chemicals in packaging materials, batteries and vehicles in line with the new information on hazards and risks that is generated e.g. under REACH. We propose that a review process should be included in these directives to regularly evaluate the existing limit values and assess the need for including additional substances in the directives