New Construction / UK / 2018 /

07 Waste

Information correct as of 18thApril 2024. Please see kb.breeam.com for the latest compliance information.

Adaptation to climate change strategy study – timing - KBCN0533

Late consideration of the climate change adaptation strategy study, might reduce the study to a ‘paper exercise’, with minimal value to the project. However, if the assessor is satisfied that there is clear justification for the strategy being developed at a slightly later stage (i.e. early RIBA stage 3) AND there is clear evidence that the strategy has achieved the intended outcomes (i.e. the later consideration has been in no way detrimental to the outcomes of the strategy study/appraisal and the benefits can still be realised on the project), then this will be sufficient for compliance. In any case, all other requirements of the issue must be met for the credits to be awarded. The requirements for the timing of the climate change adaptation strategy are intended to ensure that the benefits of these strategies are realised through early consideration.

Alternatives to composting - KBCN0465

In anaerobic digesters, organic waste is digested by micro-organisms which break down fats, oils and grease. Digesters where the only output is water that is safe to discharge into drains and sewers are acceptable alternatives to composting. Macerators which simply reduce solids into small pieces through a shredding or grinding process and flush the residue into the drainage system are not an acceptable alternative to composting.

Apportioning foundations where not all floors are assessed - KBCN0643

Where a development does not include all the storeys of a building, not all of the aggregates used in the building foundations need to be included in the assessment.  Any apportioning must be justified and calculated by a structural engineer, and it is the responsibility of the assessor to ensure that the process used is appropriate, robust and meets the aim of the credit issue.

Contractor not yet appointed at the design stage - KBCN000002

Where the contractor has not been engaged at the design stage certification, it is acceptable to award the credits based on a commitment. This commitment must be from a suitable member of the design team, and must detail the targets and criteria which must be met. Evidence must also confirm that the details in the commitment will form part of the contractual requirements. Note: This does not apply to the requirement for a pre-demolition/pre-refurbishment audit, which must be undertaken at Concept Design Stage.
12 Jul 2022 - Note added to clarify the scope of this guidance
 

Contractual agreements for Shell Only / Shell & Core assessments - KBCN0942

For Shell Only and Shell & Core (RFO Part 1, Part 2, and combined Part 1 & 2) assessments, all relevant criteria are applicable. Contractual agreements confirming future provision of spaces are not acceptable. Evidence must be provided showing waste storage space(s) that are suitably sized, dedicated and unlikely to be used by the future tenants for other purposes. While the location of the space/spaces may change when fitting out, at this stage a space that is conveniently located for the deposit and collection of operational waste must be provided.

Demolition records not available - KBCN1009

Where demolition records are missing, either wholly or in part, the credit available for diversion of construction and demolition waste from landfill cannot be achieved. This includes instances where demolition was conducted under a separate contract or by a third party on behalf of the developer.

Designed-out or integrated finishes - KBCN1066

The requirements for this credit are met when either: This issue recognises avoiding unnecessary waste of materials.
16-May-2023 - Merged with KBCN0046. Scheme applicability updated. Name updated for clarity.
 

Diversion of resources from landfill – RMP - KBCN0981

Monitoring, recording and sorting the key waste groups of non-hazardous wastes are required for this credit. Compliance with the 'Diversion of resources from landfill criteria' can be demonstrated through production of a Resource Management Plan or with equivalent documentation demonstrating that the requirements have been met.

Extension to existing buildings - KBCN1039

Facilities within the existing building can be used to assess compliance. These facilities must cater for the total volume of predicted recyclable waste arising from the new extension and existing buildings.

External works – waste reporting requirements - KBCN1379

Waste arising from external works does not need to be included within the calculations for construction resource efficiency. To do so would be incongruous with reporting waste relative to the building's floor area. This follows the logic of excluding excavation waste from this criterion. However, waste from external works should be addressed in the RMP and should also be reported in the calculations for the Diversion of resources from landfill credit, which is not reported relative to the building's floor area.

Free-standing recycling bins - KBCN1359

Free-standing internal recycling bins may be acceptable to demonstrate compliance for this Issue. These are not required to be built-in or fixed, as long as all the criteria are met, such as the provision of sufficient space in a suitable location. In cases where the recycling bins cannot be placed in the kitchen, but are located in a nearby store cupboard, for example, signage must be provided, to indicate the location of the recycling bins.

Functional adaptation strategy study – timing - KBCN0730

Late consideration of the strategy appraisal, might reduce the study to a ‘paper exercise’, with minimal value to the project. However, where the assessor is satisfied that there is clear justification for the study being developed at a slightly later stage (i.e. early RIBA stage 3) AND there is clear evidence that the strategy has achieved the intended outcomes (i.e. the later consideration has been in no way detrimental to the outcomes of the strategy study/appraisal and the benefits can still be realised on the project), this will be sufficient for compliance. In any case, all other requirements of the issue must be met for the credit to be awarded. The requirements for the timing of the functional adaptation strategy study are intended to ensure that the benefits of the study are realised through early consideration.

Home composting facilities – clarification - KBCN0927

Home composting facilities are individual composting containers placed within the kitchen area or communal space for each self-contained dwelling, bedsit or communal kitchen. These containers are either emptied into local on-site communal facilities or are collected by composting collection services run by the waste collection authority. Individual composting containers should be:
  1. Located in a dedicated, non-obstructive position.
  2. Easily accessible to all users.
  3. Durable, low maintenance and cleanable.
  4. Enclosed to manage odour and pest issues.

Labelling and signage – Where provision of waste bins is out of scope - KBCN1380

Where the provision of waste bins is outside the scope of the developer, it is clearly not possible to label the bins. In this situation, the following compliance options are available:
  1. Provide compliant signage to the storage area and label bin spaces within the storage area according to the relevant waste streams.
  2. Where future waste streams are unknown, provide compliant signage to the storage area and a written commitment from the developer to ensure that the bins and/or bin spaces are labelled.
See also KBCN1577 It is recognised that the bins may be provided by the tenant, local authority or waste management company after the time of certification.
22 Mar 2023 - Updated to align with KBCN1577 and to clarify applicability to all assessment types where providing bins is out of scope.

Limited site space for segregation and storage - KBCN1036

When a site has limited space to segregate materials on site, a waste contractor can be used to separate and process recyclable materials off-site. Manufacturers' take-back schemes can also be used to do this. In such cases, evidence to demonstrate segregation of materials was carried out to the agreed levels and that materials were reused or recycled appropriately must be produced. Such evidence could be Environment Agency (EA), Scottish Environment Protection Agency (SEPA), Environment Agency Wales (EA Wales) or Northern Ireland Environment Agency (NIEA) Waste Return Forms.

Multi-Residential: Internal recyclable waste container if waste is sorted off site - KBCN0354

Where the Local Authority or waste management company for the scheme provide evidence confirming that recyclable waste will be sorted after they have collected it from site, it is acceptable to provide one internal storage bin of a minimum capacity of 30 L rather than 3 separate internal bins. The relevant recycling scheme must collect at least 3 of the following materials; paper, cardboard, glass, plastics, metals or textiles.    

Multi-residential: Waste storage shared by more than six bedrooms - KBCN0856

Where multi-residential buildings contain communal facilities shared by more than six bedrooms, the requirement for total waste storage can be increased on a pro-rata basis to demonstrate compliance. For instance, if the standard requirement is 30L for six bedrooms, this equates to 5L per bedroom. Where assessing a flat with eight bedrooms, this requirement increases to 40L (8 x 5L). The minimum size of individual containers remains unchanged as per the criteria.

Multiple buildings on a wider estate - KBCN1065

For one or more buildings or units assessed as part of a wider estate or campus, compliance can be demonstrated through the provision of dedicated centralised storage space and waste management facilities. These must have the capacity to accommodate the recyclable waste material generated from all buildings and their activities.

Multiple developments monitoring construction waste on a site - KBCN00036

Where the same contractor is working on a site with more than one development, a single Site Waste Management Plan (SWMP)/Resource Management Plan (RMP) can be produced to demonstrate compliance, if it can be justified that separation of the waste would be impractical. Where the developments are of a similar nature, such as all new-build or all refurbishment with similar scope, the results from the whole development can be apportioned on the basis of floor area to derive the figures upon which the separate developments will be assessed. Where the buildings are not similar, the design team will need to provide calculations to demonstrate that the waste has been apportioned as accurately as possible according to the project types.
21/11/16 Clarification added in relation to dissimilar projects on the same site.

No demolition - KBCN1122

Where, under the developer's ownership, no demolition will be undertaken to enable the assessed development, the pre-demolition audit credit is filtered-out of the assessment.
To be clarified in the next re-issue of the manual.

Off-site waste sorting - KBCN0696

All schemes Where a building's recyclable waste is collected regularly and sorted off-site, the aim of this issue can be met by: This means providing evidence for all of the following:
  1. A waste management plan which provides on-site storage between collections, adequately sized based on the frequency of collection.
  2. An on-going waste recycling contract.
  3. The typical recycling rates from the waste management company.
  4. A permanent structure (or internal space) within the asset site boundary that can be converted to comply with all criteria requirements. Layout drawings must be provided showing how this space could be converted in future, including meeting all relevant criteria for: • User and vehicle access, • Area requirements for waste storage, • Appropriate size and number of containers for the expected waste streams, and • Space allowance for any additional waste processing requirements e.g. compactors, composting containers, water outlets etc.
BIU only This KBCN applies to off-site sorting for construction waste arising from fit-out activities (Answer E, BIU V6, Rsc 02). It does not apply to the storage of reusable construction products (Answer F, BIU V6, Rsc 02). This must be a permanent structure or space currently in the asset. BREEAM assesses the sustainability of the intrinsic asset. Where robust management practices may be accepted as an alternative, BREEAM still requires that the asset's facilities have the potential for future conversion to achieve compliance.
09-Feb-2024 - Requirements clarified. Applicability updated to include construction waste storage for BIU V6 Rsc 02.
17-Jan-2024 - Scheme applicability updated.
16-Apr-2018 - Wording clarified.

Operational waste – Additional requirements for multi-residential buildings with individual bedrooms and communal facilities only - KBCN1519

These criteria are intended for situations where occupants of individual rooms have access to shared kitchens, which can be used to prepare food, regardless of whether central catering is also available. In developments where all catering is managed centrally and no communal/shared kitchens are provided, these requirements do not apply. If, for example, catering is managed centrally, but there are small satellite kitchens for staff to sort/reheat food for residents, the assessor must justify whether and to what extent recyclable waste will be generated in these kitchens and demonstrate that adequate recyclable waste storage provided as appropriate.

Operational waste requirement for catering – applicability - KBCN1162

The additional operational waste storage requirement for developments which include catering is generally only applicable where a commercial scale kitchen is present. Where the design team can justify that there will be no significant waste streams from a modest facility, such as a small cafe, selling only drinks and pre-prepared snacks, the additional waste storage area identified in the default values does not need to be provided to meet compliance.

Operational waste storage sizing - KBCN0560

The dedicated space requirements given in the technical manual are default guidance, for situations where it is not possible to demonstrate the required size based on known waste streams. Compliance can, therefore, be achieved provided that it is clearly demonstrated and evidenced that there is adequate justification for the type of facilities & size of waste storage provided, and that the assessor is satisfied that the sizes and facilities meet the criteria based on the building type, occupancy and the likely waste volumes generated as a result of these.

Pre-demolition audit – criterion 1d - KBCN1168

To clarify, the comparison between actual waste arisings and waste management routes used with those forecast is to be drawn by re-visiting the pre-demolition audit, following completion of the relevant work. The intent of this criterion is to draw lessons learnt from the project under assessment to inform future improvements. 
The pre-demolition audit criteria will be clarified in the next re-issue of the technical manual.

Pre-demolition audit – demolition in a later phase - KBCN1012

Where the demolition of an existing building forms part of the works to enable the assessed development, a pre-demolition audit must be carried out to comply with the criteria, even if the demolition occurs as part of a later phase.
28/02/2018 Wording amended for clarity

Pre-demolition audit requirement - KBCN0243

Where the site demolition/clearance does not form part of the principal contractor’s works, but has been undertaken by the developer for the purposes of enabling the assessed development, a pre-demolition audit must be carried out and referenced within the SWMP as per the guidance. Where justification and robust evidence can be provided, the following exceptions may apply: This requirement seeks to encourage good practice by developers and design teams in relation to previously developed sites.
28.03.2022 Reference to pre-refurbishment audit removed, and separate KBCN1504 drafted for pre-refurbishment audit exemptions.
11.12.2019 Additional exception added to align with KBCN1257 and guidance re-structured for clarity
22.11.2017 Reference added to the pre-refurbishment audit for RFO assessments.
15.11.2017 Wording amended for clarity

Pre-refurbishment/demolition audit – late development - KBCN0537

Where the pre-refurbishment/demolition audit has not been done at RIBA stage 2/Concept Design, as required in the criteria, the credit can still be achieved. Robust evidence must be provided confirming that the timing of the pre-refurbishment/demolition audit has not compromised its ability to influence the design, consideration of materials re-use and the setting of targets for waste management. Evidence must demonstrate that this allowed decisions to be made before the start of strip-out/demolition works.
26.07.2018 Applicability of KBCN extended to include the UKNC2018 scheme.

Recyclable, general and organic waste storage – Space, labelling and segregation - KBCN1577

Strategies may vary according to the specifics of each project, their waste streams and collection arrangements. The aim of these requirements is to encourage recycling, ensuring that it is correctly sorted and to prevent cross-contamination of waste streams. Labelling the recycling area This is required to alert building users and collection agencies to the location of the recycling facility. Labelling each recyclable waste stream This can be done by labelling the bins or their dedicated space within the recycling facility, or both. Co-mingled recyclable waste This must be labelled, as above. See also additional requirements outlined in KBCN0696 General or organic waste Sufficient space for general and, where relevant, organic waste is required in addition to meeting the requirements for recyclable waste. This does not have to be within a separate facility, but if combined with recyclable waste storage, there is greater risk of cross-contamination. The following requirements therefore apply in this situation: Shell only/Shell and core projects Please also refer to KBCN1380

Recycled and sustainably sourced aggregate – Compliance prior to contractor’s appointment - KBCN1097

If the contractor has not been appointed at the time of submitting the Design Stage assessment and, as a result, there is insufficient information available to complete the Wst 02 Calculator Tool, this should be clarified in the Assessment Report. The following documentary evidence from the design team must also be provided: BREEAM does not seek to restrict the contractor’s ability to source the most economically viable recycled or sustainably sourced aggregate.
12 05 2022 Wording amended to improve clarity

Solid concrete washout - KBCN00063

Solid concrete washout waste should be included in the waste resource efficiency benchmarks.  

Speculative ceiling finishes – Substantial alterations - KBCN1141

The aim of this Issue is to avoid the unnecessary waste of materials, therefore the installation and subsequent removal of speculative finishes should not be permitted. However, BREEAM recognises that incoming tenants may need to adapt ceiling finishes to suit the requirements of their fit-out. Therefore, where ceiling finishes are installed throughout, in line with Criterion 2, the following applies: A tenancy agreement, applied to the first tenancy, should stipulate that ceiling finishes may only be modified where necessary, for example, to accommodate new partitions, lighting or other services, to replace worn or damaged components or to replace small, localised areas with a specialist ceiling to account for abnormal conditions, such as wet areas.

Suitability of waste storage facilities - KBCN0186

In situations where direct vehicular access to the recyclable waste store is limited by logistics or if size is a problem, for example inner city locations, some flexibility to the application of the criteria is allowed. The assessor can use their judgement on whether the storage space is appropriately sized and if the distance and changes in level via lifts or steps are acceptable. Convenience, H&S issues and the volume and type of waste likely to be generated must be considered.  Where the assessor deems the arrangement to be satisfactory this would be acceptable. Typically ‘accessible’ is defined as being within 20m of a building entrance. In some circumstances site restrictions or tenancy arrangements could mean it is not possible for the facilities to be within 20m of a building entrance. If, in the opinion of the BREEAM assessor it is not feasible for the facilities to be within 20m of a building entrance, their judgement can be used to determine if the facility is deemed to be ‘accessible’ to the building occupants and for vehicle collection.

Using BRE SMARTWaste tool - KBCN0236

BRE SMARTWaste may be helpful in demonstrating the construction waste benchmarks; however its use is not compulsory to achieve the credits. Reference to the SMARTWaste tool has been included in the issue as an example of a tool that can be used to manage and monitor waste generated during construction.  

Waste from temporary structures - KBCN1038

Temporary support structures, or any other materials or systems brought on site to facilitate construction of a building and that subsequently enter the waste stream (albeit for recycling) will be considered as construction waste and contribute to the construction waste generated for the development. If the support structure is reused on another site by the contractor (or another contractor) it has not entered the waste stream and, therefore, would not be included in the figures for waste generated. Reused timber formwork would be excluded in the same way.

Waste storage provision for catering - KBCN0755

As the manual states, the additional 2m2 per 1000 m2 of waste storage area provided for catering is measured against the "net floor area where catering is provided" and NOT the floor area of the catering facility. Generally, a catering facility will serve building users throughout the building. If it can be demonstrated that this is not the case, for example if part of the development is subject to a separate tenancy, not served by the catering facility, the area calculation can be adjusted accordingly. Where the net floor area is not indicative of the actual occupancy, the default values may not be appropriate. In such cases, the predicted waste streams should be calculated based on the actual occupancy and waste streams generated. This requirement accounts for the increase in waste produced by building based on the likely number of building users served by the catering facility. Please note that these default calculations are only intended for use where it is not possible to determine accurately what provision should be made based on predicted waste streams. 
15 06 2017 Wording updated to clarify

[KBCN withdrawn] ~ No floor or ceiling finishes fitted - KBCN00046

Where the developer has not specified or installed any floor or ceiling finishes, the requirements are met. This issue recognises where the potential for generating unnecessary waste of materials has been avoided. 
16-May-2023 - Merged with KBCN1066. Withdrawn.
20-Dec-2017 - KBCN wording simplified to add clarity.
 
Information correct as of 18thApril 2024. Please see kb.breeam.com for the latest compliance information.