In-Use /
BIU International Residential V6
Information correct as of 13thDecember 2024. Please see kb.breeam.com for the latest compliance information.
Alarm systems – Intent of Criterion 2 - KBCN1707
The intent of Criterion 2 is as follows:
A documented plan is in place to ensure that when the alarm is triggered, whether due to a fire or security incident, a system fault or a false alarm, building staff and occupants understand what actions to take. This must include any necessary communication with ARC staff, emergency services and other building users.
This clarification will be incorporated in the next update of the technical standard.
Assessing multiple residential buildings - KBCN1687
BREEAM In-Use has been developed as an environmental assessment method to assess existing assets. Typically, an asset consists of a single building or part of a single building. However, BREEAM In-Use provides an exception where certain criteria have been met, and this is set out in the relevant Technical Manual under the Eligibility Criterion 5 and reproduced below with clarifications noted in Italics.
The requirements to assess multiple buildings as a single asset
Criterion 5 states: An asset cannot normally include more than one building. The only exception is where several buildings meet the following criteria:
a) All buildings must be located on the same site. The site boundary must be drawn where responsibility for management or ownership of the site changes.
For multifamily assets, this means all structures within the property boundary.
For individual homes, e.g. single family, townhouses, this means the properties on which the homes are located are contiguous.
b) All buildings must have the same building function, similar performance, and be of similar design and age.
Multifamily projects, such as garden style apartments, can still be grouped together under these criteria, even if they include different unit types.
c) Building management and maintenance policies, procedures and approach must be the same across all the buildings that make up the asset to ensure consistent implementation.
Where maintenance policies, procedures, and approaches are the tenant’s responsibility through the leasing arrangements, these can vary, but overall building management needs to be the same for all properties
d) Evidence must be collated from each building that is included in the asset and where performance against the BREEAM requirements varies, the final score will be determined by the space with the lowest level of performance.
The whole data set for all buildings in the assessment must be gathered and provided to the Assessor by the Client.
Demonstrating compliance for certification
- The Client will be required to demonstrate how each criterion has been met and provide evidence to support the approach.
- The Assessor must then confirm the criteria have been met through their evidence review and on-site verification.
- Site level assessments should use a floor-area-weighted average method to confirm compliance.
- For other residential assessments involving multiple buildings, representative sampling is permitted to confirm compliance. Assessors are required to confirm that the worst-case performance was applied by the Client. Assessors are required to create and document a robust representative sampling method and demonstrate that they conducted their assessment in accordance with their methodology.
- Where the Assessor is unsure how to interpret or apply the criteria, they should contact the Technical Team for clarification using the BREEAM Projects webform before submission for certification. Where relevant, a copy of the technical clarification response should be submitted as supporting evidence.
Considerations before undertaking this approach
- The rating will reflect the worst performance of all the buildings included within the assessment.
This will limit the visibility of buildings within the grouping that may have better performance and opportunities at individual assets to improve performance. Assessing the buildings separately allows for the granularity of the assessment to provide owners with more detailed information on how improvement plans can be rolled out and the value to be gained from driving performance.
- Should the buildings be sold individually, the certification status does not transfer with the individual buildings.
The building(s) sold would need to undergo the full certification process, including benchmarking and the on-site visit with a licensed Assessor, to be considered certified and claimed by the new ownership.
- The certificate may be updated through a mid-cycle process to remove the assessed area of the building(s) sold.
This could increase the score if the building sold represented the worst-case performance. If the building removed from the certification formed the basis of the score as the 'worst-performing', the Assessor would need to complete another site visit for the mid-cycle to ensure that the new data representing the worst performance is accurate.
Asset classification – co-living developments - KBCN1568
The following is a guide only. Every co-living project will combine a varying mix of residential with managed spaces, and assessors must in all cases review the suitability of the criteria to determine the most appropriate asset classification.
Co-living features
Co-living developments generally combine:
- Self-contained residential apartments with private kitchens and bathrooms.
- Apartments are typically rented for long-term stay (i.e. for periods of more than one month).
- Managed communal facilities such as spaces for leisure, co-working spaces and common grounds.
Classification
- For NC or RFO, generally the most appropriate asset classification is 'Residential institutions - long term stay.'
- For BIU, it is generally Residential.
Using building regulation classifications as a guide
As a guide, assessors can also consider how their asset is classified according to local regulations.
For UK NC assets,
KBCN1225 provides additional clarification:
- Projects classified under UK building regulations as Part L Volume 1: Dwellings (Previously Part L1) is considered residential and covered under HQM.
- Projects classified as Part L Volume 2: Buildings other than dwellings (Previously Part L2) is considered a residential institution.
Carbon monoxide detection – Combustion appliances located outside - KBCN1586
Where all combustion appliances are located outside in the open air, no flues pass through an occupied space and there are no enclosed parking areas, the associated credits can be filtered out as per Criterion 1.
Clarification – percentage of end uses - KBCN1650
This percentage is measured by the energy consumption (kWh) of significant energy uses, not by the number of end uses.
Combined system for heating / cooling and domestic hot water - KBCN0329
It is permissible to have combined metering for a shared on-site or district system that combines heating / cooling, and domestic hot water generation.
In all cases, justification is provided in the QA report for the combined metering, and explains why it is not technically feasible to provide separate meters.
21-Sep-2022 Applicability of KBCN added to BIU V6. Amended to include district heating and cooling networks.
Condition survey – refurbishment in the last 5 years - KBCN1522
Where an asset has been refurbished, refurbished elements listed in criterion 2 can be excluded from the condition survey if:
- The refurbishment was carried out less than 5 years ago.
- The refurbishment addressed any and all major defects with the element.
- The records of the refurbishment allow asset management to effectively maintain that element.
The intent of Rsc 01 is to give asset management a complete understanding of the condition of the asset. The requirement for 5 years is to make sure that this information is relatively up-to-date, and allows effective maintenance of the asset and management of any minor defects.
All example scenarios below assume that the refurbishment was carried out less than 5 years ago. Any refurbishment works carried out more than 5 years ago must follow the full criteria of this issue.
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[accordion_block title="Scenario 1"]
A major refurbishment to a Commercial asset covered and effectively documented refurbishment to:
a. Structure.
b. Mechanical components.
c. Electrical components.
d. Plumbing.
e. Fire protection.
It did not cover:
f. Communications and life safety systems.
g. Health and safety conditions.
All major defects were resolved.
Credits for the condition survey, and for rectifying defects are awarded based on elements f. and g. only.
[/accordion_block][accordion_block title="Scenario 2"]
A major refurbishment has covered and documented all items in criterion 2. All major defects were resolved, but there are some outstanding minor defects that are being monitored and maintained by asset management.
BIU V6: This issue is filtered out as per criterion 1.
BIU 2015: The relevant credits are awarded.
Minor defects are common after major building or refurbishment works, and typical building contracts provide a period for the resolution of minor defects. As long as major defects are resolved by the refurbishment, and asset management are aware of and managing minor defects, these items can be excluded from the condition survey.
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A major refurbishment covered all elements, but there is no record of the refurbishment of mechanical and electrical components.
A condition survey covering these items is required. Relevant credits are awarded for surveying and addressing any defects for these elements.
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Converting water consumption into litres per year from new EU energy labels - KBCN1548
The following conversion factors may be used to convert the water consumption on new EU energy labels from litres per cycle (L/cycle) into litres per year (L/year):
Dishwasher: multiply water consumption figure on EU energy label by 280 (to go from L/cycle to L/year).
Washing machines: multiply water consumption figure on EU energy label by 220 (to go from L/cycle to L/year).
This follows equivalent guidance for converting energy consumption (see
KBCN1462).
25 Aug 2023 - Correction to 'typo error' for dishwasher conversion factor - previously shown as 208, now corrected to 280.
District heating / cooling / hot water – entering data into the Online Platform - KBCN1536
For assets which use district heating / cooling / hot water, information on the district systems are entered into Ene 09a and 09b.
In Ene 05 / 06 / 09, answer 'no' to first question
"Is space heating / cooling / hot water generated on-site?" then navigate to:
- Ene 09a to answer questions on district cooling.
- Ene 09b to answer questions on district heating and hot water.
A district heat network will also provide hot water, so information on the system which provides both is entered into Ene 09b.
The Online Platform differs from the manual structure, however it does not affect scoring in any way. All data entered contributes to the asset energy calculator.
Assets with on-site and off-site systems
Only answer questions on the system which provides the most signifcant heating or cooling to the asset. If an asset includes both on-site and off-site systems, choose the one which delivers the most energy annually.
Eligibility criteria – BIU International Residential V6 - KBCN1668
The Eligibility Criteria for BIU V6 Residential have been updated, and the guidance below supersedes Criterion 2 in the V6.0 technical manual:
Criterion 2)
a) Submission for certification must be a minimum of 12 months from completion of the dwellings.
AND
b) For a Part 2 assessment, 12 months’ utility consumption data must be available for a minimum of 80% of the dwellings.
AND
c) The asset must be intended to be a primary residence of the occupants.
Emergency lighting - KBCN0185
Maintained systems featuring emergency light fittings which are also used for normal operation, are assessed for this issue.
Non-maintained lighting which is only activated in an emergency can be excluded from the assessment.
NC / RFO / BIU V6 Ene 17: The aim of these credit(s) is to encourage and recognise energy-efficient fittings. Non-maintained emergency lighting will very rarely be activated and in such extremes the emergency requirements must not be compromised.
BIU V6 Hea 05: Flicker is eliminated from maintained systems only.
24-Jan-2024 - Scheme applicability updated to include BIU V6.
Ene 24 methodology - KBCN1613
This issue is scored based on % improvement relative to the
BIU V6 carbon benchmark and average annual improvement across the reporting periods.
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[accordion_block title="BIU V6 carbon benchmark"]
Standard CO2 emissions: the tailored benchmark of a UK asset.
Climate adjusted CO2 emissions: the benchmark for International assets. It adjusts the UK benchmark to account for national and regional differences.
Net CO2: the actual CO2 emissions of the asset.
Annual reduction in CO2 emissions: the annual average % figure used to score credits in Ene 24.
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Example scenario
An international BIU asset calculates the improvement in CO2 emissions across 2 reporting periods.
- CO2 emissions benchmark = 50 kgCO2e/m2 per year.
- 01-Jan-2020 to 31-Dec-2020.
CO2e emissions are 90 kgCO2e/m2 per year (1.8x the benchmark).
- 01-Jan-2023 to 31-Dec-2023.
CO2e emissions are 60 kgCO2e/m2 per year (1.2x the benchmark).
- Time between reporting periods: 3.0 years.
Calculation
- Improvement over 3 years = 1.8 - 1.2 = 0.6x improvement vs benchmark.
- 0.6 = 60%
- 60% / 3.0 years = 20%
The asset demonstrates a 20% average annual improvement vs the benchmark. It scores 3 exemplary credits.
How the calculation accounts for different reporting periods
Most assessments will report on multiple fuels in each period.
- Individual reporting periods for fuels may not align.
- Reporting periods may not begin or end at the same time each year.
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[accordion_block title = "Calculating time between reporting periods"]
Time between reporting periods is measured in days (this is converted to years in the final calculation). Time is measured from the middle of each reporting period.
If more than one fuel is reported, the individual mid-dates for each fuel are combined through a weighting calculation. The mid-date is proportionally weighted towards fuels with larger associated CO2 emissions.
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[accordion_block title = "Maximum time between reporting periods"]
The maximum time between any reporting period is 1460 days (3 years 364 days) between:
- The first recorded consumption data in the 1st period, and
- The first recorded consumption data in the 2nd period.
These dates are
not weighted by fuel consumption.
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Additional notes
- Erratum - Criterion 1. Assets where the 1st period was assessed under BIU 2015 must re-enter this consumption data into the BIU V6 Ene 24 calculator. This ensures a consistent calculation methodology for all BIU V6 assets.
- The baseline for measuring improvement (1st period performance vs benchmark) are actual asset emissions, not the benchmark. Asset CO2e emissions can exceed the benchmark in both the 1st and 2nd periods to target credits in this issue.
- The manual states that 3 years are required between periods (as this links to the BIU V6 certification cycle), however this is not a requirement for compliance. Assets can also target this issue where less than 3 years have passed (for instance after a mid-cycle certification). The calculator will adjust for the shorter gap between reporting periods.
Energy consumption reporting – Link to Man 04 - KBCN1612
The link to meeting compliance with Man 04, outlined in Ene 23 Criterion 1 is incorrect and should be disregarded.
Answer option D in Man 04 includes targets for Energy, Water and Waste. Whereas the intent of Ene 23 relates to targets for Energy only. This will be updated in the next reissue of the technical manual.
Enhanced waste collection in the asset - KBCN1528
Where the asset collects 6 or more unique residential waste streams on-site, answers G and H are available without the need for additional off-site collection points.
If the asset can provide enhanced waste collection and sorting on-site, then this is effectively the same as having a compliant collection point in the local area.
Example scenarios
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[accordion_block title="5 waste streams on-site"]
An apartment building has compliant facilities or kerb-side collection for 5 residential waste streams. There is no collection for composting or garden waste.
The asset achieves the requirements for answer C only if all relevant criteria are met. There aren't enough waste streams to meet the threshold for answer G.
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[accordion_block title="7 waste streams on-site"]
An apartment building has compliant facilities or kerb-side collection for 7 residential waste streams. There is no collection for composting or garden waste.
The asset achieves the requirements for answer C, and answer G if all relevant criteria are met.
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[accordion_block title="7 waste streams on-site, with off-site collection point within 500m"]
An apartment building has compliant facilities or kerb-side collection for 7 residential waste streams. There is no collection for composting or garden waste.
An off-site collection point within a compliant distance can collect 5 waste streams, however only 2 are unique (different from what the asset already collects on-site).
In total there are 9 unique waste streams collected on-site, kerb-side, or within a compliant distance.
The asset achieves the requirements for answer C, and answer H if all relevant criteria are met.
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Erratum – scope of issue - KBCN1498
Criterion 1 states:
"Where external lighting or car park lighting are not necessary from a safety perspective, the associated credits can be filtered out of the assessment."
What this means is:
- Where external lighting does not exist, filter out the relevant credits.
- Where car park lighting does not exist, filter out the relevant credits.
- Whether or not the lighting exists for safety reasons has no effect on credit filtering.
The inclusion of the word 'safety' in this criteria is misleading and will be removed in future versions.
28-Feb-2024 - Wording clarified.
Erratum – up to V6 – methodology – no default energy assumptions - KBCN1630
The scope of the issue applies only to systems with
significant energy use.
The methodology section states that the online platform will calculate
default values, and use this to indicate which systems are in scope.
This is incorrect, as default values are
not automatically calculated.
The energy use of each system will need to be manually estimated. This can be done based on:
- Typical benchmark values, and / or,
- Estimates based on the capacity of equipment, and annual equivalent full load hours of use.
Erratum – up to V6.0.0 – Ecological features – Answer D – planters - KBCN1543
Outdoor planters and traditional planted areas can be considered as
one feature for the purposes of Answer D, provided there is enough planting on the site to meet the intent of the issue.
To meet the requirements of Answer D, the following must be demonstrated:
- Outdoor planters, containing live plants and/or traditional planted areas
- Other planted areas such as green roofs or green walls
- Features to assist local fauna
20-Dec-2023 – The intent of this KBCN was to simplify compliance with Answer D. This has now been updated to clarify that it only applies to Answer D, thereby removing the potentially negative impact on meeting the requirements of Answer C.
24-Aug-2023 - Wording clarified. Change will be updated in the next re-issue of the manual.
Erratum – up to V6.0.0 – compliant cycle storage - KBCN1595
Criteria
Instead of answer C, criterion 3 should refer to answers D and E.
Evidence
The criteria references for this issue are incorrect, and will be corrected in the next re-issue.
Checklists and tables
- Answer D awards 2 credits for achieving the minimum number of cycle storage.
- Answer E awards 1 additional credit for achieving additional cycle storage.
The headings in Table 20 do not match these answers. Table 20 will be revised with these updated headings:
Home size |
Answer D
Minimum cycle storage
2 credits |
Answer E
Additional cycle storage
+1 additional credit |
Studio or 1 bedroom |
1 cycle space / 2 homes |
1 cycle space / home |
2 - 3 bedrooms |
1 cycle space / home |
2 cycle spaces / home |
4+ bedrooms |
2 cycle spaces / home |
4 cycle spaces / home |
Erratum – V6.0.0 – cooling efficiency parameter – EER / SEER - KBCN1560
In the asset energy calculator guidance, the parameter given for cooling efficiency is 'SEER' (Seasonal Energy Efficiency Ratio).
This is incorrect and should say '
EER'.
This affects the following tables:
|
International |
USA |
Commercial V6.0.0 |
Table 19 |
Table 18 |
Residential V6.0.0 |
Table 16 |
Table 16 |
This will be updated in the next manual re-issue.
Erratum – [BIU V6 Rsl 06] – Incorrect evidence requirements for answers G – H - KBCN1696
Please note that the requirements for the report to include 'opportunities identified' and the 'key metrics' does not align with the criteria requirements. This can therefore be disregarded.
This will be updated in the next reissue of the manual
Erratum – [BIU V6.0.0 Wat 14] – Incorrect evidence requirements - KBCN1695
The criterion 3 evidence requirement, "evidence of monitoring data" is incorrect and invalid. Assessments should not try to meet this requirement.
Criterion 3 requires the water strategy to have senior management approval. This has no relation to monitoring water consumption, which is already addressed in Wat 13 Water consumption reporting.
This error will be addressed in future updates.
Erratum – Electric Vehicles (EV) charging stations criteria - KBCN1701
In the BREEAM In-Use International Technical Manual, the Electric Vehicles (EV) charging criteria and their evidence were incorrectly referenced. The requirements for EV charging stations should read as follows
Answer G Electric Vehicles (EV) charging stations are provided for ≥5% of the car parking capacity.
Methodology
The methodology indicates the number of charging stations required should be calculated as a percentage of the total car parking capacity.
The ≥5% in Answer G indicates that at least 5% of the total parking spaces in the residential development should be equipped with EV charging stations.
If the number of charging facilities that should be supplied is not a whole number, it must be rounded up to the nearest whole number. For example, where the number of charging facilities that should be provided is calculated to be 10.2, the actual number of facilities that must be provided is 11.
Charging stations for Car Clubs cannot count towards the percentage provided for residents.
Evidence
The manual incorrectly referred to criterion 7 for the EV charging stations in the evidence section. The evidence requirement should refer to Criterion 5 and should be read as follows:
Criterion
|
Evidence requirement |
5
|
Calculations showing the percentage and number of charging stations |
5
|
Site plan showing the location and number of electric vehicle charging stations |
Evidence of no risk – Use of Approved Standards and Weightings List - KBCN0959
The current BREEAM International Non-Domestic New Construction Approved Standards and Weightings List (ASWL) can be used as evidence to demonstrate that a country has ‘no risk’ to all natural hazards apart from flooding (which is considered within POL 02 of BREEAM In-Use 2015 and Rsl 01 of BREEAM In-Use Version 6).
Any country which has a weighting of 0% for Hazards within the current ASWL can provide this to BRE Global as evidence. As flooding is not included within the Hazard section of the ASWL, it must be evidenced separately. Therefore, in order to achieve maximum credits within MAT 05 or Rsl 03, the assessment must also provide evidence that the asset is in a ‘low or zero flood risk area’ under the requirements of POL 02 (BREEAM In-Use 2015) or Rsl 01 (BREEAM In-Use Version 6).
Note: BREEAM In-Use International Assessors who are not BREEAM International Non-Domestic New Construction Assessors, will be unable to access the ASWL. In this instance please send a technical query to BRE Global outlining the country which the asset is located, and BRE Global can confirm the current weighting for that country.
This KBCN does not apply to BIU assessments under BREEAM NOR or BREEAM SE
29-Nov-2023 Clarification - N/A BREEAM NOR/SE
01-Oct-2022 Updated to apply to BREEAM In-Use Version 6
16-Aug-2016 Amended to clarify situations where there is no access to the ASWL
Fire hydrants and sprinklers – Leak detection - KBCN0680
Where it is confirmed by an appropriate project team member that it is not possible to fully meet the leak detection criteria for fire hydrants or sprinklers, an alternative approach can be implemented for these systems.
This must demonstrably meet the aim of the issue by detecting and alerting the building management to major water leaks.
Previous guidance - superseded on 30 May 2024
To meet BREEAM compliance, emergency systems such as fire hydrants and sprinklers need also to be covered by a leak detection system.
The leak detection system must cover all mains water supply between and within the building and the ‘site boundary'.
11 Sep 2024 - Applicability to BIU V6 confirmed - QN-75509-C8H8V1
30 May 2024 - New guidance introduced to clarify that BREEAM compliance should not compromise the operation of building safety-critical systems. Applicability to NC V6 standards confirmed.
Flood risk – use of flood maps only in FRA - KBCN1524
Answer option E (Commercial) or F (Residential)
If a flood risk assessment considers flooding from rivers and seas only, flood risk is zero / low, and the following requirements are met:
- There are local or national flood maps available covering these sources of flooding.
- The maps are accurate, up to date, and have sufficient detail to clearly identify flood risk for the asset.
- The maps are approved by local or national government, and based on robust data.
It is acceptable for the flood risk assessment to be carried out by a relevant member of the team. It does not require a competent individual (see manual definition) to do this.
Most sources of flooding are site-specific and require specialist input and calculation to quantify. However, flood maps meeting the criteria above can provide an acceptable level of assurance of overall flood risk from rivers or seas without the need to engage a specialist.
Answer option B (Commercial) or C (Residential)
Where the risk of flooding is medium or high, flood mitigation measures are required (criterion 3).
These mitigation measures must be defined by either:
- A local authority (the measures must be relevant to the asset).
- Or a competent individual.
The FRA can still be produced by a relevant member of the team.
Exemplary credit
This option is only available if a site-specific FRA was carried out by a competent individual, and cannot be based only on flood maps that give an allowance for climate change.
Example scenarios
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[accordion_block title="Low / zero flood risk"]
National flood maps cover flooding from rivers and seas. The flood risk from these sources is zero / low.
The compliant FRA can be produced by a relevant member of the team.
[/accordion_block]
[accordion_block title="Medium / high flood risk"]
National flood maps cover flooding from rivers and seas. The flood risk from these sources is medium / high. Flood mitigation measures are required.
The local authority provides some general flood mitigation measures for the area, but these are not relevant to the assessed asset.
Instead, a competent individual is consulted on relevant flood mitigation measures for the asset - their recommendations are recorded in the FRA.
The compliant FRA can be produced by a relevant member of the team.
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06-Nov-2024 - Answer C guidance title now corrected to point to Answer B for Commercial manuals.
Installed controls – Filtering of questions - KBCN1678
Where the building has no heating, cooling or mechanical ventilation or humidification, Ene11 can be filtered out by answering that there is none of the above to each of the relevant questions. Where some systems are applicable, the points available will be filtered out, based on the answers. For instance, where only question 1 and 2 are applicable, 6 points would be available and where only thermostatic vales are provided (Question 1 answer for 2 points), only 33% of the points would be achieved, or 1 credit as per Table 22.
In relation to the wording for questions 1 to 3, for clarity:
- Questions 1 and 2 should only be filtered out where there is no heating AND no cooling. They will still be applicable if there is only heating.
- Question 3 will only be applicable where there is both heating and cooling. It is not applicable if there is only heating.
09 August 2024 - Re-worded for clarity.
Interlock controls – clarification - KBCN1491
An interlock is a control that is wired so that when there is no demand for heating / cooling in a space, the heating / cooling generator and the associated pumps are switched off. Use of thermostatic radiator valves (TRVs) alone does not provide interlock.
Partial interlock means that the cooling and heating interlock controls are separate. However, the control function may be set up to minimise the possibility of simultaneous heating and cooling.
Total interlock means the controls are wired so that simultaneous heating and cooling is not possible. Where there are separate local heating or cooling units present, these will also need to be wired into the control system for total interlock to avoid the possibility of simultaneous heating and cooling.
Intruder alarm systems – apartment buildings or similar - KBCN1572
Scope
The scope of this KBCN applies to any residential asset that:
- Is comprised of multiple self-contained dwellings within a single building envelope, and
- Share common entrance(s) and circulation.
A typical example is an apartment building.
Principle
The asset as a whole is protected by systems that are fit for purpose to ensure the safety and security of the asset, its users and their property
Implementation
Security requirements for apartment buildings will vary greatly depending on factors such as:
- Scale and configuration.
- Access strategy.
- Local context.
- Which areas are under building management control.
Because of this, BREEAM cannot provide specific guidance on how intruder alarms and access control are configured to meet the principle.
It is the role of the assessor and a competent third party (for instance, this can be a 'competent person' as defined in Rsl 10) to evidence how this principle is achieved for the asset as a whole.
Evidence from a compliant security risk assessment carried out in line with Rsl 10 can be used to support this issue.
Management-based solutions
As a Part 1 issue, this intent must be achieved by systems which are intrinsic to the asset.
Management-based solutions (such as a concierge service, or security guards) cannot be used to achieve answer E (intruder alarm systems).
Answer F (alarm receiving centre) can only be achieved with a system that complies with Answer E.
Intruder alarms – Requirement for these to be audible when activated - KBCN1597
Where it is justified by the security consultant, project team or building management that a 'silent' intruder alarm system is more suited to the asset’s overall security strategy, this can be considered as meeting the Definition in our guidance.
LZC – Local regulations and private wire arrangements - KBCN1658
Where local regulations do not permit electricity generated by on-site renewables to be connected directly to the building, and where evidence of the relevant regulations is provided at QA, the requirement for a private wire arrangement can be waived.
Minimising flicker – scope of issue - KBCN1639
Principle
Flicker from
all lighting systems is eliminated. This means eliminating flicker in:
- All lighting within management control, common areas, and tenanted areas.
- Occupied, un-occupied and external spaces.
Only emergency lighting is excluded. See
KBCN0185.
Lighting flicker is undesirable regardless of location or length of exposure.
Commercial scope
Eliminate flicker in all lighting.
Residential scope
Eliminate flicker in:
- All communal areas (internal and external, occupied and unoccupied).
- Management offices, and all areas under management control.
Minimising watercourse pollution – Areas to be assessed - KBCN1633
Criterion 2 should be interpreted as follows:
The intent is to provide a list of areas that are likely to present a risk of watercourse pollution. All the listed areas must be considered, however, where a listed area is not present, or it is present but poses no risk of watercourse pollution, this should be justified with supporting evidence.
Where the development does not include any of the listed areas, or none of the areas present poses a risk of watercourse pollution, justification and evidence must be provided and this issue should be filtered out, in line with Criterion 1.
ModeScore Sustainable Transport certification - KBCN1705
Achieving
ModeScore Gold or Platinum certification can be submitted as part of the supporting documentation
to award credits for implementing sustainable transport options,
provided the BREEAM criteria were targeted, as follows:
Scheme |
Issues |
Credits |
BREEAM International NC 2016 and V6 |
Tra 03a Alternative modes of transport |
2 + Exemplary credit |
Tra 03b Alternative modes of transport |
2 + Exemplary credit |
Tra 04 Maximum car parking capacity |
1 |
BREEAM UK NC 2018 and V6 * |
Tra 02 Sustainable transport measures |
10 |
BREEAM Int RFO 2015 |
Tra 01 Sustainable transport solutions |
5 |
Tra 04 Maximum car parking capacity |
2 |
BREEAM UK RFO 2014 |
Tra 01 Sustainable transport solutions |
3 |
Tra 03 Cyclist facilities |
2 |
Tra 04 Maximum car parking capacity |
2 |
BREEAM In-Use Commercial and Residential (International and USA) |
Tra 01 Alternative modes of transport |
8 |
Tra 02 Proximity to public transport |
3 |
Tra 04 Pedestrian and cyclist safety |
2 |
* BREEAM UK NC 2018 and V6 credits can be awarded provided the transportation assessment and travel plan (criterion 1) are met
When the assessor submits a ModeScore certification as evidence, they should include their report and highlight the BREEAM criteria or credits that were targeted.
About ModeScore Sustainable Transport certification:
ModeScore assess and certify sustainable transport facilities and services in buildings. ModeScore encompasses ActiveScore within its assessment criteria, covering four pillars of sustainable transportation while incorporating accessibility into each:
- Public Transportation
- Environmentally-Friendly Private Vehicles
- Active Transportation
- Site-Wide Mobility
ModeScore evaluates the connectivity potential of any building in any location, offering four levels of certification with a total scorecard of 120 points. ActiveScore (Travel Facilities) counts for 10 points:
- Certified (0-39%)
- Silver (40-59%)
- Gold (60-79%)
- Platinum (80-100%)
See more information and details at https://modescore.com/
Night-time operation – requirement for controls - KBCN1048
Projects
or areas of an asset which operate at night-time can adapt or omit the requirement to provide controls or presence detection to align with the building’s hours of operation.
This could, for example, include service yards or car parks.
The aim of this Issue is to reduce the energy use for external lighting and should not interfere with the building’s operation.
02 Oct 2024 - Updated to clarify the scope of the this guidance and applied to NCV6 and BIU.
Occupant control – spaces requiring user controls - KBCN0170
This guidance is intended to clarify the types of area for which user controls are required or would be considered beneficial.
Zoning is required in all areas of the asset where specified in the assessment criteria. Please refer to the specific requirements of the applicable BREEAM standard to interpret this guidance appropriately.
User controls required
Spaces where users are expected to have independent control over their environment.
- Owned spaces: small rooms for a few people.
For instance, cellular offices, owned spaces in residential assets.
- Temporarily owned spaces: where occupants expect to operate the environmental controls while they are there.
For instance, meeting rooms and hotel bedrooms.
- Shared spaces.
For instance, multi-occupied areas such as open-plan offices or workshops.
User controls not required
Spaces where users are not expected to have independent control over their environment.
- Managed spaces: where environmental control is expected to be centrally managed.
For instance, atria, circulation areas, concourses, entrance halls, function halls, restaurants, libraries, and shops.
- Occasionally visited spaces.
For instance, storerooms, bookstacks in libraries, aisles of warehouses, toilets.
14-Dec-2022 - KBCN applicability updated to include BIU. Wording clarified, and amended for compatibility with BIU criteria.
On-site LZC – whole site shared connection - KBCN1424
To be recognised in BREEAM, the on-site Low and Zero Carbon (LZC) technology must have a direct physical connection to the assessed asset.
OR
Where the LZC technology is;
- Located on the same site,
- Is owned and managed by the same organization as the assessed building, and
- Where it is impractical to physically connect the assessed building to the system,
It is acceptable to allocate the renewable energy generated proportionally as a calculation of the asset's predicted energy consumption compared to the total energy consumption of the whole site.
To allocate renewable electricity by proportional consumption:
- Obtain the total annual renewable electricity generated on-site.
- Exclude all renewable electricity which has been exported to the grid.
- Determine the respective electricity consumption of all assets on the whole site (predicted for new builds and measured for existing assets).
Where consumption data is missing, renewable electricity must not be allocated to the assessed asset. In this case, it is assumed that all electricity consumed is sourced from the grid.
17-Jan-2024 - Applicability BIU V6 Ene 13 removed, as this approach is not applicable to assessing the area of PV fitted.
21-Dec-2022 - Applicability to In-Use V6 confirmed.
24-Aug-2022 - Applicability to UKNC V6 confirmed.
Presence detection – illuminated signs - KBCN1671
The requirements for presence detection do not apply to illuminated signs.
In BIU V6, presence detection requirements are included as part of automatic energy saving controls. All other requirements in this criteria must still be met.
Recognising future performance - KBCN1538
BREEAM In-Use recognises an asset's operational performance
at the time of certification.
Compliance
cannot be based on commitments to improve the performance of an asset in the future.
Where changes to an asset are made during a 3-year certification cycle:
- BREEAM In-Use V6 allows the asset's mid-cycle performance to be updated and reflected in an updated certificate.
- Legacy versions of BREEAM In-Use recognise updated performance via re-certification.
Residential eligibility criteria – clarification on occupancy levels [superseded] - KBCN1523
01 Nov 2014 This guidance is now superseded. Please refer to KBCN1668
Resources inventory – Scope - KBCN1667
The inventory only needs to include resources that belong to the asset owner (or those which the asset owner or manger is responsible for maintaining or replacing). It does not need to included tenant-owned fittings and furnishings
Risk assessment – flooding is the only natural hazard - KBCN1552
Where:
- Flooding is the only natural hazard identified and,
- The flood risk assessment (FRA) from Rsl 01 is used as evidence for this issue,
then Answer D ('the asset is in an area where no risks exist') is only available where the FRA shows zero or low flood risk from
all sources of flooding.
Assessing flood risk from rivers and seas only does not cover all risks.
Safe pedestrian routes: definition, measurement and verification - KBCN0238
Definition
Safe pedestrian routes include pavements and safe crossing points, which may be controlled or, for example, be identified by tactile paving, a crossing island or a dropped kerb. An element of judgement may be required, in which case justification should be provided.
Measurement
Distances could be measured, for example, along a pavement, across a road at a safe crossing point and along the pavement on the other side. The distance should not be measured diagonally across a road, following the most direct route.
Evidence from Google Maps or other digital sources may be used to indicate routes and distances, provided that the scale is appropriate and clearly indicated.
Verification
The assessor’s site inspection is an important aspect of the assessment of this issue as it must confirm that all relevant information is current and should include photographs of any key areas. This may also help to identify safe crossing points or hazards which may not be apparent from a desktop study.
For BREEAM NC and RFO assessments, Google Streetview may be acceptable as evidence to demonstrate safe pedestrian routes and the presence of key features or amenities at Design Stage only. Such information must be verified as above for Final Certification.
07 Mar 2024 - No changes have been made. This appears as 'updated' due to an administrative error.
11 Jan 2024 - Wording re-structured for clarity
19 Dec 2023 - Applicability to BIU V6 confirmed
Shower with multiple shower heads - KBCN0855
To calculate the water use of a shower with more than one shower head, one of the following should be done:
- If all of the shower heads can be turned on at once, the flow rates should be added up.
- If the shower heads can only be used one at a time, the highest flow rate should be used
22 Feb 2024 - Applied to BIU, BREEAM NC and RFO standards
Single and Multiple Certification options - KBCN1430
BIU Residential provides flexible options to allow as many residential buildings as possible to be rated and receive a certificate. These include:
Apartments
- Multiple certificates, one for each individual apartment unit
- A single certificate for all the apartments only
- A single certificate for all the apartments and the common area
Houses
- Multiple certificates, one for each individual house unit
- A single certificate for all the houses
Benefits of the different certification options
Multiple certificates – These show the performance of each residential unit. This can show the difference in scoring and rating between units, which could be used for sales purposes or as a way of targeting specific units for improvements. When opting for multiple certificates, the rating of the best performing units will not be limited by the performance in other units.
Evidence must be collated from each building that is included in the assessment and where performance against the BREEAM requirements varies, the final score will be determined by the apartment or home with the lowest level of performance.
Single Certificates – These show the performance of the apartment(s) or house(s) as a whole. While performance has to be documented for each dwelling, BREEAM Projects includes features which help streamline this process.
Which certification route is right for my Asset?
When assessing just the Asset Performance in BREEAM In-Use Residential v6, the choice of certification option is up to the client. However, if Management Performance is included in the scope of assessment then the differing data requirements will determine which certification option the project needs to follow. These differing data requirements are driven by the energy consumption data available.
The flow diagram below can be used as a guide to determine the appropriate certification route for your project, given the energy consumption data available.
The scope of the energy data available will typically be more variable for an apartment building compared to houses. Houses tend to be individually metered, and therefore certification options are more open to client choice.
Note: Any asset without compliant consumption data will not be able to achieve all of the credits within Management Performance (e.g. the Operational Energy Calculator and Water)
If further assistance is required, please contact BRE at
[email protected]
24 Apr 2024 - Paragraph headed 'Benefits of the different certification options' updated for clarity and KBCN applied to BREEAM In-Use USA Residential
20 July 2021 Amended for clarification and flow diagram updated
Smoking policy – External areas - KBCN1680
The criteria do not require that the asset provide a designated external smoking area.
The intent of Specific Note 1 is that the asset management encourage compliance with the no smoking policy by identifying areas where building users are not prohibited from smoking. However, where it is justified that no such areas can be identified within proximity of the asset, this requirement can be disregarded.
Sub-metering technologies – Compliance Principle - KBCN1561
Where it can be demonstrated that alternative sub-metering technologies can meet or exceed the capabilities of systems set out in the BREEAM guidance, subject to approval, these can also be considered compliant.
It is the role of the Assessor and the project team to provide evidence and justification in a compliance principle query (see
KBCN1555).
The following metering standards or technologies are currently recognised as alternatives to pulsed output meters:
- M-bus.
I.e. systems that comply with the EN 13757 series of standards.
Also includes systems complying with the OMS (Open Metering System) standards.
Sub-metering using non-intrusive load monitoring (NILM) systems - KBCN1710
Non-intrusive load monitoring (NILM) systems cannot be used to demonstrate compliance for the sub-metering credits within BREEAM. Hardware-based sub-meters must be installed. NILM systems are generally retrofit systems which can be easily removed and are not integral to the building or installed building services.
Systems serving <10% overall floor area - other affected issues - KBCN1542
The methodology for Ene 01 states:
"Heating / cooling systems can be excluded from the calculation where the heated or cooled area equates to less than 10% of overall floor area."
Systems which heat or cool < 10% overall floor area
are not assessed in:
- Ene 01 Building services.
- Ene 05 Cooling.
- Ene 06 Heating.
Ene 01, 05 and 06 all feed into the asset energy calculator and so their inputs must be consistent. All other issues relating to these excluded systems are still assessed such as:
- Ene 11 Installed controls.
- Ene 15 and 16 Monitoring energy issues.
- Pol 03 Local air quality.
- Pol 04 Global warming potential of refrigerants.
Thermographic survey – Standards for test method - KBCN1578
The appropriate international standard for thermographic surveys is ISO 6781:1983
Thermal insulation – Qualitative detection of thermal irregularities in building envelopes – Infrared method.
The following are acceptable alternative standards:
- EN 13187:1998 Thermal performance of buildings – Qualitative detection of thermal irregularities in building envelopes – Infrared method
Using water from natural underground sources to offset water consumption - KBCN00094
Water from natural underground sources (for instance aquifer water accessed via boreholes) cannot be used to offset:
- NC / RFO: potable water consumption.
- IU: utility supplied water consumption.
A significant amount of water used for public consumption is already drawn from aquifers. Private boreholes may be drawing water from the same sources as public utility companies.
27-Mar-2024 - Title and text updated to broaden definition. Scheme applicability updated.
View out – Calculating the glazing to wall ratio - KBCN1506
This should be calculated based on the glazed area of window, expressed as a percentage of the area of the external wall in which the window sits.
Where the ceiling height of the room is unusually high, relative to the window height, the wall area can be calculated based on a standard ceiling height for the building type.
Volume Approach – Site visit requirements - KBCN1644
This guidance applies only to assessments for clients who have entered into a formal agreement with BRE to enter the Volume Approach.
The aim of the Volume Approach is to assist clients with large numbers of assets, and their assessors, to conduct assessments in a robust manner, whilst also taking a practical view. From the clients’ assets that have entered the process, BRE will identify which assets may undertake a virtual site visit.
The assets and their assessments cannot be new to the BREEAM In-Use process and must be identified and communicated to BRE prior to undertaking the site visits.
The requirements of the virtual site visits are as follows:
Gathering evidence for site assessments:
In cases where BRE has identified an asset can undergo a virtual site visit, the assessor is not required to personally visit or gain access to the site, they can use the following methods:
- Appoint a suitable individual, for example a main contractor or asset manager, to undertake a formal site assessment on their behalf. The appointed individual would be expected to provide a robust account to the assessor of evidence in place of their own site assessment report. We would expect the report to contain photographs and/or virtual tour stills from the building and be signed off by both the appointed individual and assessor.
- For assessment issues relating to external spaces beyond the site, we will accept stills/images from Google Street View (or equivalent), provided it is demonstrated that such evidence is current.
- Desk-based evidence will be accepted where evidence demonstrates that the criteria are being met as far as possible without a site assessment.
It is important to note that where one of the above 3 options has been selected, the assessor is responsible for assessing the evidence and for the awarding of any credits.
Timing of workshops, testing and other subsidiary evidence submissions:
Given the widespread availability of remote communication technologies, it is generally possible to undertake the majority of activities relating to our assessment criteria without the need for face-to-face contact or site assessments. With respect to workshops, the key consideration is that they take place at a time when they have a meaningful impact and achieve the aim of the criteria.
With respect to subsidiary, third party assessments such as ecological site inspections or audits, desktop surveys based on available information (e.g. planning surveys, agent’s reports, photographs, Google Earth), can be used as an alternative provided there is enough material for a confident recommendation and/or outcome to be achieved.
Washer dryers - KBCN0699
Where a washer dryer is specified, the water consumption figure for the wash and dry cycle should be used.
The drying cycle of a washer dryer is taken into account because it usually uses water during this drying process (e.g. for cooling during the drying cycle) and in some cases, this water usage can be significant.
18-Nov-2022 - Updated to apply to BREEAM In-Use Version 6
Washing machines and dishwashers – Water consumption data - KBCN1571
The water consumption data used to demonstrate compliance may be based on the lowest full wash cycle (i.e. not a pre-wash cycle, for example).
Waste streams – clarification - KBCN1526
Scope
The focus of the criteria is on
recyclable materials only. Any facilities / spaces for managing recyclable materials must be
in addition to spaces / facilities for managing general waste.
Definition
“Waste streams are flows of specific waste, from its source through to recovery, recycling or disposal. Waste streams can be divided into two broad types:
- Streams made of materials (such as metals or plastics).
- Streams made of certain products (such as electronic waste or end-of-life vehicles).”
Source
For BREEAM, a waste stream is a material / product with its own recycling process. This means each stream needs to be separated from other materials before it can be effectively processed into new materials / products. This separation can happen in the asset, or (in the case of co-mingled waste) after collection from the asset.
Residential waste streams
In most cases, this is defined by how it will be how be sorted and collected by municipal waste authorities. Where no local guidance exists, the list below may be used as a guide.
Recyclable waste streams (answer option C in BREEAM In-Use Residential V6):
- Paper and cardboard.
- Glass.
- Plastics.
- Metals.
- Wood and wood-based products.
- Oils.
- Batteries.
- Electrical and electronic equipment.
Compostable / recyclable waste streams (answer option D in BREEAM In-Use Residential V6):
- Food waste.
- Garden waste.
Commercial waste streams
Commercial assets will generate specialised waste streams specific to the asset's function. These are typically:
- Generated consistently, and in large volumes.
- Are specifically separated for recycling.
In these cases, waste streams such as metals, plastics and paper / cardboard may be sub-divided into specialised waste streams where they meet the above.
Example scenarios
[accordion]
[accordion_block title="Scope"]
A vehicle repair workshop generates the following waste streams:
- Metals.
- Paper / cardboard.
- Plastics.
- Engine oils.
- General waste.
The engine oils and general waste cannot be re-processed into other usable materials. Only 3 recyclable waste streams can be considered for BREEAM assessment.
[/accordion_block]
[accordion_block title="Residential"]
The local authority collects co-mingled waste for the asset. This waste mixes together:
- Metals.
- Paper and cardboard.
- Plastics.
This co-mingled waste can be counted as 3 waste streams.
[/accordion_block]
[accordion_block title="Commercial"]
A supermarket consistently generates large quantities of cardboard packaging. This cardboard forms a significant portion of recycable waste generation. It is baled up and collected separately by a specialised waste contractor.
In this case, cardboard waste can be considered a separate waste stream from paper.
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[/accordion]
18-Jan-2024 - Clarified list of residential waste streams (separated compostable waste streams and added relevant answer options).
Water consumption reporting – Link to Man 04 - KBCN1611
The link to meeting compliance with Man 04, outlined in Wat 13 Criterion 1 is incorrect and should be disregarded.
Answer option D in Man 04 includes targets for Energy, Water and Waste. Whereas the intent of Wat 13 relates to targets for Water only. This will be updated in the next reissue of the technical manual.
Water strategy – Replacement and Schedule - KBCN1673
Replacement
The intent is that there is a programme in place which identifies any planned refurbishments and confirms that, where relevant, the works will include upgrading high water-consuming fittings and appliances with low water-consuming equivalents.
This does not require the systematic replacement of all fittings and appliances. However, it must also include a commitment to upgrading the efficiency of existing fittings and appliances when they reach the end of their service life.
Schedule
This may include specific fittings and appliances with low water consumption, or it can be based on a performance specification that these must meet, e.g. the flow rate or efficiency rating.
Information correct as of 13thDecember 2024. Please see kb.breeam.com for the latest compliance information.