MRF Regulations: Difference between revisions
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The [[MRF Code of Practice]] applies to any facility (known as 'Qualifying [[MRF]]s') that receive over 1,000 tonnes or more of 'Mixed Waste Material' - the definition of which is [[Waste|waste]] originating from households or [[Waste|waste]] from other sources if it is similar to [[household Waste|household waste]] in terms of its nature or composition<ref name="WRAP">[https://wrap.org.uk/sites/default/files/2020-10/WRAP-MF%20Sampling%20Guidance%20April%202014.pdf/ Sampling and Testing Guidance for Material Facilities] WRAP 2014</ref>. | The [[MRF Code of Practice]] applies to any facility (known as 'Qualifying [[MRF]]s') that receive over 1,000 tonnes or more of 'Mixed Waste Material' - the definition of which is [[Waste|waste]] originating from households or [[Waste|waste]] from other sources if it is similar to [[household Waste|household waste]] in terms of its nature or composition<ref name="WRAP">[https://wrap.org.uk/sites/default/files/2020-10/WRAP-MF%20Sampling%20Guidance%20April%202014.pdf/ Sampling and Testing Guidance for Material Facilities] WRAP 2014</ref>. | ||
Wastes 'similar to [[Household Waste|household waste]] are those typically found in a [[Household Waste|household waste]] stream such as plastic bottles (typically ≤5 litres), pots, tubs and trays ([[PTT]]s) used for food packaging (typically ≤525cm in their longest dimension), flexible plastic packaging, [[Glass|glass bottles]] and jars, food tims, steel or aluminium drinks cans, [[Paper|newspapers and magazines]] and cardboard packaging<ref name="WRAP" />. | Wastes 'similar to [[Household Waste|household waste]]' are those typically found in a [[Household Waste|household waste]] stream such as plastic bottles (typically ≤5 litres), pots, tubs and trays ([[PTT]]s) used for food packaging (typically ≤525cm in their longest dimension), flexible plastic packaging, [[Glass|glass bottles]] and jars, food tims, steel or aluminium drinks cans, [[Paper|newspapers and magazines]] and cardboard packaging<ref name="WRAP" />. | ||
For non-household waste to fall under the definition of Mixed Waste Material the two or more fractions of [[Glass|glass]], [[Metal|metal]], [[Plastic|plastic]] or [[Paper|paper]] that make up the largest proportion (≥50%) of the waste should be similar in composition to those wastes described above. | For non-household waste to fall under the definition of Mixed Waste Material the two or more fractions of [[Glass|glass]], [[Metal|metal]], [[Plastic|plastic]] or [[Paper|paper]] that make up the largest proportion (≥50%) of the waste should be similar in composition to those wastes described above. |
Revision as of 14:16, 11 October 2021
The MRF Code of Practice (MRF CoP) was published in February 2013 and required all material recovery facilities over a certain size to measure the quality of their inputs and outputs[1].
Introduction
The MRF Code of Practice (MRF CoP) was published in February 2013 and required all material recovery facilities over a certain size to measure the quality of their inputs and outputs. The MRF CoP introduced a new requirement to make all results from these tests publically available, for example to businesses buying the material as well as to Local Authorities and others who supply material to the MRFs [1]. It did not set any minimum quality standards.
MRF Code
The MRF Code of Practice is enacted through Sch 9 of the Environmental Permitting (England and Wales) (Amendment) Regulations 2014 which has now been transposed into the Environmental Permitting (England and Wales) Regulations 2016. The requirements took effect from 1 Oct 2014 and required that MRFs to whom the regulations applied must[2]:
- sample and test the materials they receive and send out
- record the information
- report every 3 months to the regulator
The MRF Code of Practice applies to any facility (known as 'Qualifying MRFs') that receive over 1,000 tonnes or more of 'Mixed Waste Material' - the definition of which is waste originating from households or waste from other sources if it is similar to household waste in terms of its nature or composition[3].
Wastes 'similar to household waste' are those typically found in a household waste stream such as plastic bottles (typically ≤5 litres), pots, tubs and trays (PTTs) used for food packaging (typically ≤525cm in their longest dimension), flexible plastic packaging, glass bottles and jars, food tims, steel or aluminium drinks cans, newspapers and magazines and cardboard packaging[3].
For non-household waste to fall under the definition of Mixed Waste Material the two or more fractions of glass, metal, plastic or paper that make up the largest proportion (≥50%) of the waste should be similar in composition to those wastes described above.
Facilities likely to be in scope
The facilities that are likely to be within the scope of the regulations are:
- Material Recovery Facilities (MRFs) sorting household dry recyclables
- Commercial Waste sorting operations and transfer stations where materials similar to household wastes are sorted into two or more Specified Output Materials (e.g. a MF sorting plastics and cans would be in scope although one sorting a single stream such as paper and card would not)[3].
References
- ↑ 1.0 1.1 Letsrecycle, 2013
- ↑ Material Facilities:how to report on mixed waste sampling, DEFRA 2018
- ↑ 3.0 3.1 3.2 Sampling and Testing Guidance for Material Facilities WRAP 2014