Stay Informed
Follow us on social media accounts to stay up to date with REHVA actualities
R.C.A. van Holsteijn | H.J.J. Valk | J. Laverge | W.L.K. Li |
VHK Research, Delft, Netherlandsr.van.holsteijn@vhk.nl | Nieman Raadgevend Ingenieurs BV, Utrecht, Netherlands | Ghent University, Building Physics,
Construction and Service Group, Belgium | VHK Research, Delft, Netherlands |
Up until
today the performance of ventilation systems in residential buildings remains
largely unaddressed. It is generally assumed that compliance with building
codes results in an acceptable indoor air quality (IAQ). It is also assumed
that the various types of code-compliant ventilation systems perform
comparably. Field research however demonstrates that both assumptions are
incorrect: IAQ-levels can be far from adequate and there are large differences
in ventilation performance between systems in dwellings [1, 2, 7, 8, 9,10,11].
With energy performance standards demanding increased airtightness levels and
reduced natural infiltration [9,10], there is a serious need to assess the
actual performance of ventilation systems.
In most
countries, building regulations on ventilation are based either on the capacity
of the ventilation provisions to be installed, or on a minimum air-flow for the
whole building. Air-exchange performance levels in the individual habitable
rooms and wet rooms, based on the operating reliability of selected ventilation
provisions, their controls, outdoor wind speed, building airtightness and
occupant behaviour, are not considered, despite the fact that these parameters
are crucial for occurring IAQ-levels.
In the
Netherlands, when the Dutch Standard Committee was requested to develop a new
ventilation standard for the Dutch building codes, it was decided to include a
performance assessment method for ventilation systems. It was also proposed to
base this ventilation performance assessment method on the methodology that was
developed by VHK and U-Gent in consultation with the Residential Working Group
of EVIA. This methodology was presented on the 2017 AIVC conference in
Nottingham [5]. The methodology needed adaptations to fit the demands of the
Dutch building regulations [12] under public law. This paper describes both the
methodology and how it has been adopted for the implementation in the draft new
prNEN 1087, Ventilation systems for buildings.
This standard will be published for public comments in spring 2019.
Building
codes differ significantly where ventilation rates and IAQ-metrics are
concerned, even in EU-countries and despite the fact that national standards
bodies participate in CEN workgroups and technical committees. Typically,
some countries use the number of persons as basis for the ventilation rates,
while others use floor-area as a metric or the carbon dioxide-level and/or the
RH-level.
The common
denominator in the different approaches is the fact that a certain airflow
capacity of the ventilation component or -system is to be installed. The
assumption is that when code compliant airflow capacities are installed –
regardless of the type of system – code compliant air exchange rates are
achieved. The logical consecutive assumption is, that all code compliant
ventilation systems perform comparably on achieved air exchange rates and
consequently on IAQ. However, both field surveys and model research clearly
indicate that the impact the type of ventilation provisions and its controls
have on the actual occurring air exchange is significant [2,3,9,11] As a result
there is a wide range of IAQ-levels that are actually achieved and the
IAQ-level is often significantly worse than aimed at in building codes and
standards.
On another
note, no distinction is made for ventilation needs during absence and presence
of inhabitants. During absence ventilation is only required to prevent
accumulation of building- and interior products emissions, while during
presence ventilation would be aimed at inhabitant-produced emissions. In other
words, ventilation during absence or presence of inhabitants has different
aims.
Using IAQ
directly as a performance indicator requires a clear understanding of what good
IAQ actually is. All polluting substances would then have to be defined as well
as their allowed threshold values and required ventilation rates.
Recent
research, including work in the AIVC-setting, time and again gives new
understanding on parameters that define a healthy IAQ [14, 15, 16]. It is often
concluded that more research is needed to enlarge the degree of certainty of
the advised ventilation-rates. This approach, although in itself valuable, is
not expected to lead to new ventilation strategies or largely different
ventilation rates than those in the current standards and building codes. Most
clearly it is stated by Carrer et. al. [15] that: ‘… none of the mentioned standards present a
coherent, clear and consistent strategy on how to design ventilation rates that
refer to and respect directly health requirements ...’
However,
there is consensus that regarding IAQ, source control (or in other words selecting
the right building material, furniture and decorative products) is the primary
strategy [14, 15]. In addition, ventilation plays a key role in reducing the
remaining exposures [14]. In this perspective the most recent recommended
ventilation rates must be perceived. It is clear that RH-levels nor CO2-concentrations match with the complexity of IAQ. But as indicators for
the air exchange rates for respectively wet spaces and habitable spaces, the
parameters are most adequate and consequently most widely used [13, 14].
Notable in this context is that, in the HealthVent guidelines with regard to the ventilation system, it is emphasised that proper design, operation and maintenance are relevant for compliance of the system to the thus defined ventilation rates [15]. The effectiveness of the system (are the intended air exchanges actually achieved in all wet and habitable spaces) is not mentioned.
The main document in Dutch building code is Building Act (Bouwbesluit), currently Bouwbesluit 2012, last revised in July 2018 [12]. In this document the ventilation rates for all building types are specified. For all building, excluding residential, the ventilations rates are defined by the number of people the building is designed to use. For residential buildings and single dwellings, the rates depend on the area of ‘verblijfsgebied’ a difficult to translate typical Dutch conception, which is best referred to as ‘habitable space’. In general, it is the total surface of all habitable rooms, without the distinction of the type of use of the rooms. For wet or exhaust spaces it is however possible to differentiate between bathroom, toilet and kitchen.
The Dutch Bouwbesluit gives minimum capacities for ventilation of habitable spaces and exhaust spaces. For schools, office buildings and other utility buildings, the requested capacity depends on the amount of people the building is designed for, as stated in the calculation when applied for a building permit. In this paper we will focus on residential buildings. The ventilation requirements in Bouwbesluit 2012 for all dwellings are (and unchanged since mid-80s) are presented in Table 1.
Table 1. Ventilation requirements according Bouwbesluit 2012.
Type of room | Minimum ventilation capacity to be installed |
habitable spaces | 0,9 l/s·m² (with a minimum of 7 l/s per room |
toilet | 7 l/s |
bathroom | 14 l/s |
kitchen | 21 l/s |
The capacity should be calculated in accordance with NEN 1087:2001. The Dutch Standard Committee was requested to revise this standard and decided to include a performance assessment method for ventilation systems, based on preliminary research [1, 10].
To actually achieve the requested ventilation rate, all influencing factors which affect air exchange in a room should be evaluated and taken into account. The rate of air exchange is considered to be representative for the amount of fresh air and the transport of pollutants, independent of the nature of the pollutants in a specific situation. Thus, the ventilation system and degree of air exchange it provides, is representative for the probability that a healthy indoor air quality is present during occupation. The ‘quality of a ventilation system’ is the result of the characteristics of all components including controls, the rate of influence of the building and surroundings and the probability of proper use by the inhabitants.
During the development of the revised Dutch ventilation standard, the authors proposed to base the requested quality assessment method on the methodology that was developed by VHK and U-Gent in consultation with the Residential Working Group of EVIA. This methodology was presented on the 2017 AIVC conference in Nottingham [5]. For this assessment method the following definition is adopted for the air-exchange performance of residential ventilation systems: ‘the ability to achieve the requested air exchange in each room of a dwelling for the purpose of extracting and/or diluting concentrations of all hazardous and annoying substances’ [5].
Obviously, also this approach has its disadvantages. It will not be possible to predict the exact IAQ in a specific room in a specific building under all circumstances. It is limited to an educated and substantiated expectation of to what extent and with what probability the requested air exchange can be achieved. In that sense, this approach fits with the generally phrased goals for ventilation in the Dutch building act, which states: ‘a building has such a provision for air exchange that an unfavourable indoor air quality is prevented’. [13; art 3.29 lid1, translation by the authors].
The methodology that is developed and proposed [6], assesses the actual occurring air exchange rates on room type level during presence and absence. This specific Air Exchange Performance (AEP) determines to which extent the ventilation system is able to remove and/or dilute pollutant concentrations in the various rooms, especially during presence when exposure occurs. Compared to current practice, where only the air exchange rate over the building is assessed, this represents a major step towards more relevant ventilation performance assessment. Current practice after all does not differentiate between the places in which the air exchanges occur nor between periods of presence or absence. This implies that with current assessment methods, a system that mainly ventilates the corridor, is similarly valued as a system that ventilates the habitable spaces. Likewise, no distinction is made between air exchanges that occur during presence or absence; both are considered equally relevant. Clearly current practice does not lead to a proper assessment of the ventilation performance [14].
Based on the principle that is described in the paper ‘Methodology for assessing the air-exchange performance of residential ventilation systems’ [5], a calculation method is proposed, that assesses the air exchange rates that occur in both habitable spaces and exhaust spaces during periods of absence and presence.
Initial focus on
residential ventilation systems -
Only applicable to ventilation systems that are properly installed (in
accordance with prevailing buildings codes, national practitioner guidelines
and manufacturer guidelines) -
Air-exchanges for the purpose of extracting cooking fumes are excluded
from the assessment (dedicated solution (cooker hood) is default) -
Mechanical ventilation systems using continuously alternating flow
directions are excluded from the scope (no representative field research
available) -
Only technical system features will serve as input for the assessment |
Figure 1. Scope of proposed assessment method:.
In the
assessment method, two room types are used, with a matching ventilation strategy:
Habitable Spaces (HS: living rooms, bedrooms, study,
etc.), with long exposure of inhabitants to polluting substances in the indoor
air during presence. The reference ventilation strategy is to accommodate
air-exchange during presence, where supply of sufficient fresh outdoor air is
key, and the exhaust is adjusted accordingly. During absence, basic ventilation
rates are required to prevent accumulation of building- and interior products
emissions.
Exhaust Spaces (ES: kitchen, bathroom, toilet,
laundry room), with short exposure of inhabitants, but possibly high humidity
levels which are leading. The reference ventilation strategy is the extraction
of sufficient air so that moisture/odour is removed. Also, during absence of
inhabitant's extraction of air is needed until humidity levels are below
threshold values, to be followed basic ventilation rates.
The
following technical specifications and parameters of the ventilation system are
needed:
·
Type
of air-exchange provisions (direct/indirect, driving force)
·
Installed
maximum airflow capacity (limiting factor for achievable air exchange rates)
·
Type
of operation and/or controls (affects systems ability to achieve requested
air-exchanges at the right time in the right place)
·
Type
of filtration of supply air (indication of filtration performance for
situations where quality outdoor air is insufficient).
The
reference air exchange rates (AER) will be based on the air exchange rates that
are described in prEN16798-1 [4]
Figure 2. Illustration explaining the
ventilation performance assessment method.
The
European Ventilation Industry Association distinguishes seven different
ventilation system types in the various European markets. These system types can
be identified by the type of air exchange provision they use in habitable
spaces and exhaust spaces. The Dutch Standards Committee intends to implement
this clear classification in the new Dutch prNEN1087. Table 2gives a short
overview of the characteristics of these system types by describing the type of
the air exchange provisions.
Table 2. Ventilation System Type (VST)VST.
roomtype | air exchange
provision | abbrev. | ||
1 | habitable spaces | supply | natural direct supply | NDS |
extract | natural indirect extract | NIE | ||
exhaust spaces | supply | natural indirect supply | NIS | |
exhaust | natural direct exhaust | NDE | ||
2 | habitable spaces | supply | mechanical indirect supply | MIS |
exhaust | natural direct exhaust | NDE | ||
exhaust spaces | supply | mechanical indirect suply | MIS | |
exhaust | natural direct exhaust | NDE | ||
3 | habitable spaces | supply | natural direct supply | NDS |
extract | mechanical indirect extract | MIE | ||
exhaust spaces | supply | mechanical indirect supply | MIS | |
exhaust | mechanical direct exhaust | MDE | ||
4 | habitable spaces | supply | natural direct supply | NDS |
exhaust | mechanical direct exhaust | MDE | ||
exhaust spaces | supply | mechanical indirect supply | MIS | |
exhaust | mechanical exhaust | MDE | ||
5 | habitable spaces | supply | mechanical direct supply | MDS |
extract | mechanical indirect extract | MIE | ||
exhaust spaces | supply | mechanical indirect supply | MIS | |
exhaust | mechanical direct exhaust | MDE | ||
6 | habitable spaces | supply | mechanical indirect supply | MIS |
exhaust | mechanical direct exhaust | MDE | ||
exhaust spaces | supply | mechanical indirect supply | MIS | |
exhaust | mechanical direct exhaust | MDE | ||
7 | habitable spaces | supply | mechanical direct supply | MDS |
exhaust | mechanical direct exhaust | MDE | ||
exhaust spaces | supply | mechanical indirect supply | MIS | |
exhaust | mechanical
direct exhaust | MDE |
The
proposed assessment method distinguishes between periods of occupancy and
periods of absence. As a consequence, additional information on occupancy
patterns is requested (to be based on typical dwelling occupancy data).
Next, for
the air exchange provisions used in the various ventilation system types
mentioned in Table 1, the controls that are applied
determine to what extend ventilation provisions are switched to the requested
capacity during periods of occupancy and absence. For ventilation provisions
that depend on natural driving forces, the probability of the availability of
these driving forces (wind, stack or both) need to be taken into account. These
are determined, based on physical principles and statistic data.
Finally,
the building or dwelling itself has an influence on occurring air exchanges
rates, leading to the necessity to incorporate certain building parameters (air
tightness and number of habitable- and wet spaces) into the calculation method.
Based on
this data, the probable occurring air exchange rate (AER) is determined. By
dividing the probable AER by the reference AER (as specified in Building Codes)
the Air Exchange Performance is obtained.
The
methodology needed adaptations to fit the demands of the Dutch building Act
[12] under public law. Although the method itself is at first a private
addition to the national new NEN1087 standard, in coordination with the
relevant Department (BZK) the method will hopefully be adapted to fit in the
public building code in the future.
Four main
adaptations were made:
·
Abandonment
of the differentiation in type of habitable rooms.
·
Adjustment
of the reference AER to the requested ventilation according to Bouwbesluit 2012 the removal of the related categories for
Air Exchange Performance classes.
·
Determination
of the occupancy patterns.
·
Removal
of the ventilation performance label.
The
abandonment of the differentiation in type of use (living room, bedroom or
study) makes the method less specific for a specific dwelling and specific use,
but is essential to accommodate the principles of the Dutch building act.
Next step
will be to fit the first AEP-results of this new assessment method with field
research results and the outcome of multi-zone airflow models, thus providing a
substantiation for the use of this assessment model and the versatility of the
new AEP- and AER parameters. Based on that outcome, the Dutch standard
committee will decide on the implementation in the new standard NEN 1087.
Furthermore, the results will be presented to CEN-TC 156, for evaluation,
comments and possible input for further development, both in the methodology
itself as eventually in the EN 13141- and EN 16798-series.
The
adjustments that were necessary to make the methodology suitable for use in
building regulation, resulted in more generic performance values for habitable
spaces, but nevertheless not less valuable. It is therefore essential to point
out that the performance assessment method cannot be used to predict the
IAQ-levels that can be expected, but that it is intended to compare ventilation
systems on their ability to achieve the requested air exchanges in the right
place on the right time. With it a relatively simple method will become
available within the context of building regulations, making it possible to –
apart from ventilation capacity requirements - set limit values for performance
indicators.
The authors
wish to thank Marco Hofman of ISSO for his
contribution.
This
article is based on a paper presented at the 39th AIVC
Conference, held on 18-19 September 2018 in Antibes Juan-Les-Pins, France.
[1] Van Holsteijn,
R.C.A, Li, W.L.K., Valk, H.J.J., Kornaat,
W., (2016), Improving the IAQ-& Energy Performance of Ventilation Systems
in Dutch Residential Dwellings, International Journal of Ventilation, Vol. 14,
No. 4, p.363-370.
[2] Laverge, J., Delghust, M., Janssens, A., (2015) Carbon dioxide
concentrations and humidity levels measured in Belgian standard and low energy
dwellings with common ventilation strategies, International Journal of
Ventilation, Vol.14, No. 2, p.165-180.
[3] Van Holsteijn,
R.C.A., Knoll, B., Valk, H.J.J., Hofman,
M.C. (2015). Reviewing Legal Framework and Performance Assessment Tools for
Residential Ventilation Systems, Proceedings of the 36th AIVC Conference,
Madrid, Spain.
[4] Final draft prEN 16798-1:2016,
Energy performance of buildings – Part 1: Indoor environment input parameters
for design and assessment of energy performeance of
buildings addressing indoor air quality, thermal environment, lighting and
acoustics – Module M1-6.
[5] Van Holsteijn,
R.C.A., Laverge, J., Li, W.L.K., Methodology for
assessing the air-exchange performance of residential ventilation systems,
Proceedings of the 38th AIVC Conference, Nottingham, UK.
[6]
Van Holsteijn,
R.C.A., Laverge, J., Li, W.L.K., Methodology for
assessing the air exchange performance of residential ventilation systems –
Documentation, EVIA, 2017 (not published).
[7] Tappler, P.,
Hutter, H.P., Hengsberger, H., Ringer, W. (2014),
Lüftung 3.0 – Bewohnergesundheit und Raumluftqualtität
in neu errichteten energieefficienten Wohnhäusern,
Österreichisches Institut für Baubiologie und Bauökologie (IBO), Wien, Austria.
[8] McGill, G.M., Oyedele,
L.O., Keeffe, G.K., McAllister, K.M., Sharpe, T. (2015), Bedroom Environmental
Conditions in Airtight Mechanically Ventilated Dwellings, Conference
Proceedings Healthy Buildings Europe May 2015, The Netherlands, Paper ID548.
[9] Sharpe, T., McGill, G., Gupta,R., Gregg, M., Mawditt, I., (2016), Characteristics and Performance of
MVHR Systems, A meta study of MVHR systems used in the Innovative UK Building Perfromance Evaluation Programme, Report published by Fourwalls Consultants, MEARU and Oxford Brookes University.
[10] Kornaat, W., Bezemer, R., (2016), Voorstudie voor herziening NEN1087. TNO-rapport TNO2016R10956
[11] Van Holsteijn, R.C.A., Li, W.L., namens Consortium Monicair deel A, (2014), Resultaten van een monitoring onderzoek naar de binnenluchtkwaliteit- en energieprestaties van ventilatiesystemen in de woningbouw, Eindrapport WP1a.
[12] Bouwbesluit 2012, (2018), Besluit van 29 augustus 2011 houdende vaststelling van voorschriften met betrekking tot het bouwen, gebruiken en slopen van bouwwerken (Bouwbesluit 2012), Stb. 2011, 416, laatstelijk gewijzigd bij het Besluit van 22 juni 2018, houdende wijziging van het Bouwbesluit 2012 inzake de aansluiting op het distributienet voor gas, Stb. 2018, 197.
[13] De Gids, W.F., (2011), Ventilatie van ruimten ten behoeve van personen, Achtergronden van de eisen, TNO-rapport 060-DTM-2011-00610,2011.
[14] Borsboom, W., De Gids, W., Logue, J., Sherman, M. Wargowski,
P., (2016) Residential ventilation and health, AIVC Technical Note 68.
[15] Carrer, P., de
Oliveira Fernandes, E., Sabtos, H., Hänninen, O., Kephalopoulos, S., Wargowski, P., (2018), On the development of heath-based
ventilation, Guidelines: Principles and Framework.
[16] Jones, B., (2017), Metrics of Health Risks
from Indoor Air, Ventilation Information Paper 36, INIVE EEIG.
Follow us on social media accounts to stay up to date with REHVA actualities
0