Stay Informed
Follow us on social media accounts to stay up to date with REHVA actualities
Pawel
Wargocki | Corinne
Mandin | Wenjuan Wei | Carlos
Espigares |
Jana
Bendzalova | Olivier
Greslou | Mathieu
Rivallain | Johann
Zirngibl |
Energy
renovation of the European building stock is crucial for achieving the
reduction of CO2 emissions. The emissions
associated with the buildings are estimated to amount as much as 35% of the
total CO2 emissions. This action is essential in
mitigating climate change and its effects. The conversion rate of building
stock into environmentally friendly low-energy alternative is however still
quite low in Europe and remains at the level not higher than 1% to 2% annually
(Artola et al., 2016). This conversion rate cannot
underpin the very ambitious targets set by the European Commission regarding
the reduction of energy use and non-fossil fuel energy production, as well as
the overall intention for quick decarbonization of building stock in Europe.
The rate at which new buildings are erected cannot produce sufficiently high CO2 reduction. Improving the energy performance of the
existing buildings through their deep-energy renovation seems, therefore, at
present to be the most efficient method for achieving decarbonization of
building stock. The rate at which renovations are made must consequently be much
higher than today.
Among
different impediments of the low conversion rate of European building stock
into buildings with low-energy use is the cost of performing the renovation and
the long period for the return on the investments necessary to perform the
renovation – there are financial benefits resulting from low energy use in
buildings, but they are relatively low compared to investments required to
improve the energy performance of a building. Additional justification and
incentives for energy renovation of buildings, not only related to the
environmental impact and energy use, are therefore required to boost the
renovation rates far above the present low rates. Besides, straightforward and
transparent procedures are required to support the energy renovation of
buildings. They will secure that the intended energy savings are reached, that
they are properly communicated and monetized and that no other risks exist that
will limit the expected benefits from the renovation process.
To address
the matters mentioned above the project ALDREN has been conceived and launched
in 2017. The project was granted by the European Commission within the Horizon
2020 Programme (aldren.eu). ALDREN stands for “Alliance for Deep Energy
Renovation”. The main objective of ALDREN is to develop the operational
methodology for advancing energy renovation of buildings; offices and hotels
are the target buildings. The major elements (modules) of ALDREN methodology
comprise the development of:
·
a
European harmonized energy performance rating, offering comparability and
transparency across the EU;
·
an
energy performance verification protocol to enhance confidence (“you got what
has been promised”), building value and management tools;
·
a
health and well-being assessment framework offering the integration of indoor
air quality, comfort and health in the scope of deep energy renovation;
·
and
a method for financial valuation of both energy and non-energy benefits the
latter comprising, for example, an increased building value or productivity in
renovated buildings.
All these
elements are embraced in the Building Passport and are additionally used to
produce the Renovation Roadmap. They respectively collect and present all
information regarding the energy performance of a building and energy renovation
process, as well as provide recommendations and alternative solutions for the
most effective, successful and financially healthy and beneficial energy
renovation process. The elements of ALDREN methodology presented above are
developed so that they can be used as stand-alone modules, but of course, the
overall intention of ALDREN is that they are used together forming the
so-called ALDREN method for deep-energy renovation. The method is expected to
create a enough incentive to increase the rate at which
renovations are carried out. Besides, this method is additionally expected to
become a backbone of EVCS, the European Voluntary Certification Scheme, which
has been proposed and considered by the Energy Performance of Building
Directive (EPBD) (2010) as a market-driven vehicle to boost the energy
renovations in the non-residential building sector entailing as much as 25% of
the gross building floor area in Europe. Finally, it is believed that ALDREN
method will become sufficiently attractive and straightforward so that it can
be adopted partially or entirely by any other certification scheme already in
use. The structure of ALDREN indicating the consolidation with EVCS is shown in
Figure 1.
Figure 1.
ALDREN in a nutshell, six tasks for consolidation and adaptation of an EVCS
(European Voluntary Certification Scheme) based common language.
As
indicated by the above bullet points, one of the elements of ALDREN method for
the deep-energy renovation of offices and hotels is the development of a
protocol for assessment of indoor environmental quality (IEQ) in building
undergoing the energy renovation. One reason for the inclusion of this module
in the ALDREN method is the direct requirement of EPBD (2010). EPBD is
mandating that “Member States should support energy
performance upgrades of existing buildings that contribute to achieving a
healthy indoor environment” and that each long-term renovation strategy
shall encompass “an evidence-based estimate of expected
energy savings and wider benefits such as those related to health, safety and
air quality”. Another reason why the assessment of IEQ was included is
that it allows estimating the potential additional benefits resulting from the
renovation process that are not related to reduced energy use. They include
among others the improved IEQ conditions in a building that has undergone
energy renovation compared with the condition prior to renovation, improved
well-being, comfort, health and productivity of building occupants, the
increased market value of a building, lease renewal or time needed to lease the
space, and alike. The subsequent economic benefits of these improvements are
expected to be several times higher than those resulting from reduced energy
(e.g., Wargocki and Seppanen,
2006). These additional benefits, often called non-energy benefits, create a
powerful argument and incentive to perform energy renovation because their
inclusion results in significantly lower pay-back times of the investments and
because the resulting profits can be achieved much quicker and can be much
higher than those that are associated only with lowering of energy use.
There are
different protocols used to quantify IEQ in buildings including both the
objective measurements of the components of IEQ, i.e., parameters describing
the thermal, acoustic and luminous (visual) environment and air quality, and
the subjective ratings of building occupants providing among others the
information on their satisfaction with IEQ. However, no standard protocol
exists describing, for example, the minimum number and type of measurements
that need to be carried out to evaluate IEQ adequately in buildings.
Consequently, rather than adopting one of the existing approaches for measuring
IEQ, it has been decided that ALDREN should develop the protocol for assessing
IEQ in buildings that undergo energy renovation with the focus on offices and
hotels which are the target building typologies of ALDREN. This protocol should
be applicable in buildings prior to and after the energy renovation is completed.
It has additionally been decided that such protocol should not differ
considerably from the measuring protocols that are already in use, especially
it should not differ much from the protocols proposed by different schemes that
are used for providing the sustainability certification of buildings; it was
feared that too original and unconventional protocol might limit its use in
practical applications. It was also decided that ALDREN protocol for IEQ
measurements should only include objective measurements. Although subjective
measurements have many advantages and provide information that cannot be
obtained by the objective measurements, e.g., building occupants can express
directly whether they are satisfied with IEQ or not, the use of subjective
measurements was troublesome and ambiguous. An important argument justifying
this opinion was that there is no standard questionnaire that can be proposed
and applied for rating IEQ by building occupants. Another valid argument was
that there are too many factors that can impact and/or modify the responses of
occupants and that it is difficult to control them well and make the proper
adjustments when the occupant ratings are analysed. Consequently, the ratings
of IEQ made by occupants in different buildings may not be comparable, which
would breach the original intentions and objectives of ALDREN.
To assist
the process of developing the protocol for assessing IEQ in buildings
undergoing energy renovation, the methods for assessing IEQ proposed by various
certification schemes were examined and summarized. It was done mainly to learn
which IEQ parameters are measured when buildings are given the sustainability
certificate. An inventory of parameters used to characterize IEQ in different
certification schemes was made (Wei et al., 2019), and some results are shown
in Table 1. To make this inventory, thirteen green
building (GB) certification schemes were examined, among which nine were
European and four non-European ones. Because the ALDREN project is addressing
the European building stock, the summary mainly focused on GB schemes developed
in European countries because they were expected to accord with EU regulations,
standards, climate and with European traditions for construction, building
culture and heritage. Some GB schemes developed in non-European countries were
also included in the summary because they are used globally, and thus also in
Europe. Only the information available for public that could be retrieved from
the documents posted on the certification schemes webpages was used to create
this summary; the standards referred to by surveyed GBs were not examined. The
focus was on indicators used to assess IEQ in offices and hotels. However, if
no specific information for these types of buildings was provided, the
indicators recommended for any types of buildings were retrieved from GB
schemes.
Table 1.
IEQ indicators commonly used by Green Building certification schemes.
IEQ indicator | Level(s) | HQE | OsmoZ | BREEAM | KLIMA | DGNB | LiderA | BES | ITACA | WELL | LEED | CASBEE | NABERS |
Thermal environment | |||||||||||||
PMV | x | x | x | x | x | x | x | ||||||
PPD | x | x | x | x | x | ||||||||
Air
relative humidity | x | x | x | x | x | x | |||||||
Operative
temperature | x | x | x | x | x | ||||||||
Air speed | x | x | x | x | x | ||||||||
Acoustic environment | |||||||||||||
Ambient
noise | x | x | x | x | x | x | x | x | |||||
Reverberation
time | x | x | x | x | x | x | x | x | |||||
Indoor air quality | |||||||||||||
Ventilation
rate | x | x | x | x | x | x | x | x | x | x | x | ||
TVOC | x | x | x | x | x | x | x | x | x | ||||
Formaldehyde | x | x | x | x | x | x | x | x | x | x | |||
CO2 | x | x | x | x | x | x | x | ||||||
CO | x | x | x | x | x | x | |||||||
PM10 | x | x | x | x | x | x | |||||||
PM2.5 | x | x | x | x | x | ||||||||
Ozone | x | x | x | x | x | ||||||||
Visual (luminous) environment | |||||||||||||
Illuminance
level | x | x | x | x | x | x | x | ||||||
Daylight
factor | x | x | x | x | x | x | x | ||||||
Spatial
daylight autonomy | x | x | x | x | x |
Nineteen
indicators characterizing thermal environment were identified. Among them, the
most commonly used ones were Predicted Mean Vote (PMV), Predicted Percentage
Dissatisfied (PPD), room operative temperature, room air relative humidity, and
air speed. Twenty indicators characterizing acoustic environment were
identified. Among them, the most commonly used ones were ambient noise and
reverberation time. Thirty-nine indicators characterizing IAQ were identified.
Among them, the most commonly used ones were ventilation rate and concentration
of total volatile organic compounds (TVOC), formaldehyde, carbon dioxide (CO2), carbon monoxide (CO), particulate matter (PM10 and
PM2.5), ozone, benzene, and radon. Twelve indicators characterizing luminous
(visual) environment indicators were identified. Among them, the most commonly
used ones were illuminance level, daylight factor, and spatial daylight
autonomy.
The summary
of IEQ indicators was used to select IEQ parameters that should be included in
the protocol for assessing IEQ in buildings undergoing energy renovation that
is proposed by ALDREN. Not all parameters listed in Table 1
were selected, and this table does not include all parameters that were
eventually included in the measuring protocol. The method for rating of IEQ in
buildings proposed by ALDREN contains both the measuring protocol for the
selected IEQ parameters as well as the rating of overall IEQ level using a new
IEQ index called ALDREN TAIL index, in short TAIL. The measuring protocol and
an index allow thus repeatability, comparability as well as similar standard
rating metric, all originally called for in the proposed ALDREN method.
TAIL is
shown in Figure 2. TAIL stands for the thermal (T),
acoustic (A) and luminous (L) environment, and indoor air quality (I), the four
cardinal components characterizing IEQ. Each component is assessed separately,
and the quality of each component is provided by TAIL. The quality level is
depicted by different colors, green standing for high
quality, yellow for medium quality, orange for moderate quality, and red
representing low quality. TAIL also provides information on the overall quality
level of the indoor environment. This level depends on the quality of the four
components of IEQ: T, A, I and L. The overall quality is expressed by the Roman
numbers, I standing for high quality, II for medium quality, III for moderate
quality, and IV for low quality. These levels match the quality levels
prescribed by the standard EN16798-1 (2019), one of the standards supporting
EPBD (2010).
Figure 2.
ALDREN TAIL index, in short TAIL.
The quality
levels of the components of TAIL are determined by performing measurements of
different parameters characterizing IEQ. Twelve parameters are selected:
temperature for rating the quality level of T, sound level for A, ventilation
rate, concentration of CO2, formaldehyde, PM2,5,
radon and benzene, relative humidity and visible mold
level for I, and illuminance level and daylight factor for L. The measured
values are compared with the reference values, and then their quality levels
are determined. The reference values are set either to match the standard
EN16798-1 (2019) or the WHO Air Quality Guidelines (2006, 2010). The detailed
protocol for measuring the selected twelve parameters was developed, including
the selection and a minimum number of measuring points, details regarding the
accuracy of instrumentation, as well as analysis of measuring results.
Ten
parameters used to characterize IEQ are measured. Visible mold
is assessed by visual inspection, and the daylight factor is assessed by
simulations. The protocol recommends the measurements and assessments in
seasons with extreme conditions, which for most European regions comprises at
least heating (winter) and non-heating (summer) season. Simulation of some IEQ
parameters have been considered as a supplement or to replace the measurements.
However, simulations require many assumptions, especially in the case when the
original information regarding the construction materials used in the existing
building undergoing renovation is unknown. Consequently, it was felt that
performing measurements would provide a more accurate estimate of the actual
IEQ level in a building. In addition to that, it is worth mentioning that many
IEQ parameters simply cannot be simulated at present.
The
measuring protocol and the index developed by ALDREN are currently subjected to
testing and preliminary validation. Testing is made during pilot measurements
carried out by ALDREN project in existing buildings that have undergone energy
renovation. The index is reviewed by the project partners and different
building stakeholders. Consequently, the index and the protocol presented in
this article are not in their final version - they can still be revised and
supplemented if the project continues its activity that is scheduled to end in
the spring of 2020. There are few additional parameters considered for
measurements and few protocol modifications, including the method for
determining the overall IEQ level.
Artola I,
et al. Boosting Building Renovation: What potential and value for Europe? Study
for the Itre Committee of the European Parliament
(2016)
(http://www.europarl.europa.eu/RegData/etudes/STUD/2016/587326/IPOL_STU(2016)587326_EN.pdf)
EPBD
(2010). Directive 2010/31/EU of the European Parliament and of the Council of
19 May 2010 on the energy performance of buildings (recast). Official Journal
of the European Union, 18(06), 2010.
Wargocki, P., & Seppänen,
O. (2006). REHVA Guidebook no. 6, Indoor Climate and Productivity in Offices, How to integrate productivity in life cycle cost analysis of
building services. Rehva.
Wen
et al. (2019) Summary of indoor environmental quality indicators for hotels and
offices – the basis of the IEQ indicators in ALDREN method, in the Press.
World
Health Organization. (2006). WHO Air quality guidelines for particulate matter,
ozone, nitrogen dioxide, and sulfur dioxide: global
update 2005: summary of risk assessment (No. WHO/SDE/PHE/OEH/06.02). Geneva:
World Health Organization.
World
Health Organization. (2010). WHO guidelines for indoor air quality: selected
pollutants.
Follow us on social media accounts to stay up to date with REHVA actualities
0