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Moisture Management of Building Envelopes: A Moisture Index Approach to Characterizing Climates for Moisture Management of Building Envelopes

May 15, 2004

INTRODUCTION
Recent history has documented the premature
failures of building envelopes in various
regions of North America – notably on
the West Coast and the East Coast [1], [2].
The problem appears, to some extent, to be
influenced by climate. The MEWS (Moisture
Management of Exterior Wall Systems)
Consortium project, undertaken by the
Internatonal Research Council of Canada
(IRC) and its partners, has addressed this
issue in detail. The objective was to develop
guidelines for moisture management strategies
for wall systems to meet user requirements
of long-term performance and
durability for the wide range of climate
zones across North America [3]. The focus
was on wood-frame buildings of four stories
or less, exposed to a range of outdoor climates.
Effective moisture control implies both
minimizing moisture entry into the system
and maximizing the exit of moisture that
does enter, so that no component in the
system stays “too wet” for “too long.” But
what is “too wet” and “too long”? The strategy
for answering these questions was
based on predicting the moisture management
performance of wall systems as a
function of climate, wall construction, and
material properties through mathematical
modeling. A large parametric study was
undertaken using a state-of-the-art twodimensional
transient heat, air, and moisture
transport model [4].
A major task, among others, was to
determine, using climatic data, which North
American locations require special
provisions to mitigate moisture
related problems.
There are several different schemes
for classifying the world’s climates. Most of
the climate classification schemes have
subdivisions and boundaries partly based
upon temperature and rainfall parameters,
which have significance in terms of some
non-climatic feature such as vegetation or
human habitability. If one disregards nonclimatic
phenomena, it is difficult to provide
meaningful temperature-rainfall limits of
climatic types. The majority of classification
schemes, therefore, are of an “applied”
character. Traditional climate classifications,
although useful, are too coarse to be
of use to building science practitioners.
An approach to climate classification
based on a Moisture Index was developed.
The Moisture Index relates the wetting and
drying potential of a climate. A provisional
map of North America was produced using
the Moisture Index approach, mapping the
continent into zones related to potential
moisture problems. A key task was to determine
which years to use as input for a parametric
hygrothermal study of wall systems
and climate. Moisture Reference Years were
selected using the Moisture Index approach
developed. The objective of this paper is to
report on the development of the Moisture
Index approach, evaluate the measure by
comparing it to a hygrothermal response
indicator, and give two examples of its
application. The first is a case study in producing
a moisture risk hazard map, and the
second illustrates the selection of Moisture
Reference Years for a parametric study
using a hygrothermal simulation tool.
A Moisture Index for Building Envelopes
There exist several maps to help designers
and builders. Some, such as Lstiburek’s
[5] and Russo’s [6], are based on combinations
of temperature and rainfall that are of
particular concern to designers and
builders. Other maps, such as Boyd’s [7] are based on wind-driven rain and are used
O C T O B E R 2 0 0 4 IN T E R F A C E •
with respect to durability issues. Maps such
as Setliff’s [8] explicitly characterize climate
with respect to the risk of decay in exterior
wood in above-ground structures.
Another approach to climate classification
is based on defining a Moisture Index.
Bailey [9] provides a succinct definition of a
Moisture Index. A Moisture Index compares
wetting and drying, or more specifically,
evaporation. Moisture Indices have an
established history in climate zoning for
such applications as agriculture and vegetation
in general. Drying can be a significant
factor when assessing the required
level of protection for walls exposed to rainfall,
making the Moisture Index potentially
preferable to construction-related temperature-
rainfall approaches to climate zoning.
In the most general form, a Moisture Index
can be written as a function of a wetting
component and a drying component.
The wetting
component might be
defined by one of the following
measures or functions of wetting:
annual or annual directional,
Driving-Rain Index
(m2/s-year), average annual
rain load on a wall, or rainfall
on the ground (kg/m2-year).
Ideally, a comparative index
of wetting should measure
the amount of water that a
wall system must manage by deflecting,
draining, or drying. On the other hand,
there is some merit in staying independent
of the wall construction and in choosing the
simplest and most readily available measure.
Thus, unless otherwise indicated, the
Wetting Index (WI) is the average annual
rainfall on the ground (kg/m2-year).
Setting aside deflection and drainage as
attributes of wall construction, we are left
with drying as the other component of MI.
Measuring drying is a little more complex
than using rainfall for the wetting component
(see the MEWS Task 4 Final Report
[10]). A simple measure of drying that
relates to evaporation is the difference
between the humidity ratio at saturation
and the humidity ratio of the ambient air.
This is a measure of the capacity of the air
to take up water vapor, calculated from the
dry bulb temperature
and relative humidity.
This is similar to the Π factor
method described by Hagentoft [11].
Unlike the Π factor method, however, the
drying function does not use the assumed
characteristics of the wall. The Drying Index
at time t is simply the difference between
the humidity ratio (alternatively the mixing
ratio) at saturation, wsaturation, and the humidity
ratio at ambient conditions, wout
(Equation 1). The Drying Index for a location
can be calculated from Equation 2.
The next step is to combine WI and DI
into a Moisture Index MI, a single measure
of climate severity (from the standpoint of
moisture management of a wall system).
Perhaps the simplest option is to divide WI
by DI, so that a higher number always indicates
a greater moisture load:
MI – WI/DI
For comparative measures, it is convenient
to normalize the index and to eliminate
or ignore units, particularly as they are
different for WI and DI. For instance, in
comparing MI for a given set of locations,
each value can be normalized, or scaled, by
dividing by the largest MI in the set.
Another option for MI, which was in fact
used in the MEWS implementation,
requires WI and DI to be scaled to lie
between 0 and 1 for the set of locations
being compared, before they are combined
as shown in Equation 4. MImews, therefore,
has a theoretical maximum value of 1.4
Figure 1 shows the west to east progression
of the two versions of Moisture Index
for several major Canadian cities. The
hypothesis is that the higher the value of
MI, the greater the potential risk for
moisture-related damage. The values for
WI/DI have been normalized to the maximum
value in the data set, St John’s NF,
which has a “raw” MI of 1.17. A clear distinction
is made between the coastal and
continental climates. Lower values are
apparent in more continental locations.
The normalization of MImews took into
account a much larger set of North
American climates. If the range of WI and DI
is changed significantly, a different ranking
will result. The west to east progression of
MImews for the 13 Canadian cities is similar to
the simple ratio definition but, due to the
different normalizing scheme and a larger
sample set size, the relative magnitudes of
Figure 1: West to east progression of MI and MImews for several Canadian cities. the two measures differ.
1 2 • I N T E R F A C E O C T O B E R 2 0 0 4
What arguments can be given
in favor of the more complex definition of
MI? If one thinks of wetting and drying as
the balancing of a moisture budget for the
wall system, there may be a preference for
MImews. It can also be pictured as the distance
from the origin of an x-y plot of one
minus the normalized DI versus the normalized
WI, Equation 4. Severity of the
Wetting Index increases from zero to one.
The severity for one minus the Drying Index
also increases from zero to one. The potential
for moisture problems increases with
increasing values of x and y. A point near
the origin (0, 0), consequently would have
the lowest potential for moisture-related
problems while the point furthest from the
origin (1,1) would have the highest.
The MImews for each city in the sample set
was calculated as the distance from the origin.
This is shown in Figure 2. The moisture
indices for 41 candidate cities were calculated
from hourly data. The cities were
selected to represent the range of interest of
the MEWS partners. Out of these 41 locations,
seven were selected for the paramet-
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O C T O B E R 2 0 0 4 IN T E R F A C E •
Figure 2: A plot of 1 – normalized Drying Index versus normalized Wetting Index.
ric study. Two cities from the top third of
the ranked list, two from the middle third,
and three from the bottom third of the list
were selected for more in-depth analysis.
The seven locations chosen for detailed
analysis are given in Table 1 as well as the
range of climate types covered by the selected
locations.
The approach used in the MEWS project,
which was to define the Wetting Index
using annual average rainfall, has two
advantages. First, developing wetting indices
from annual rainfall is more practical
and the data are readily available.
Considerably less time and fewer resources
are involved compared to generating these
values from hourly concurrent rain and
directional wind data. The Moisture Index
can be reduced to three elements: temperature,
humidity, and rainfall. This approach
can also be applied where hourly data are
not available. This is shown in the section
describing the development of a provisional
map. Second, the normalization scheme
can help to set quantifiable limits on the
MImews that can be used for climate zoning.
Relationship Between Hygrothermal Response
and Moisture Index
The ultimate test of a Moisture Index is
its success as an indicator of climate severity
with respect to the potential for moisturerelated
damage. Recall that the hypothesis
is that the higher the value of MI, the greater
the potential risk for moisture-related
damage. Figure 3 shows the relationship
between the Moisture Index for the seven
cities considered and a proposed wall
response measure known as “RHT,” for a
wood-framed, stucco-clad wall with OSB
sheathing.
Wall Response
The definition of this wall response measure
is provided in the MEWS summary
findings report [3], but a brief description of
RHT geared to wood decay is as follows.
Fungal attack of wood-based materials
in a wall requires sustained conditions of
high moisture content combined with
above-zero temperatures. Hence, a singlenumbered
indicator RHT is formed by multiplying
(RH – RHthreshold) by (T – Tthreshold) and
summing only non-zero values for two years
for a target region in the wall. The target
region for the wall in Figure 3 was a thin
lamina of wood at the top of the base plate
inside the insulation cavity. Relative
humidity of the wood is determined from
the moisture content of the wood and calculated
using a sorption isotherm. For the
study, the RH (relative humidity) threshold
was 95%, and the T (temperature) threshold
was 5ºC. The thresholds are an estimate of
the limiting conditions for the onset of wood
decay. For other types of moisture damage,
different thresholds could be used, e.g., 5ºC
and 80% RH for mold; 0ºC and 95% RH for
corrosion. The hypothesis here is that the
higher the value of RHT (95), the higher the
likelihood of the onset of wood decay.
Wall Response versus MI
In Figure 3, increasing climate severity
(MI) is measured along the x-axis, while the
increasing risk of moisture-related damage
(RHT) is measured along the y-axis. The figure
shows three curves. The lowest curve
(blue) shows the response of a wall without
water ingress; and the top curve (red), the
response of a reference wall with water
ingress through a deficiency. The middle
curve (green) shows the response of wall
with water ingress but with materials chosen
to promote drying to the exterior.
Details pertaining to the construction of
the wall, choice of materials, amount of
location of water entry, and air leakage are
discussed at length in the summary findings
of the MEWS project [3]. When there is
Figure 3: The relationship between climate severity and wall response for 3 scenarios.
Location Main Driving- Climate Type Lstiburek [5] Rank,
Rain Direction (Russo) [6] MImews
Wilmington, NC North Hot, Wet Mixed Humid 1.13
Seattle, WA South Mild, Wet Cold 0.99
Ottawa, ON East Cold, Wet Severe Cold 0.93
Winnipeg, MB North Cold, Dry Severe Cold 0.86
San Diego, CA South Hot, Dry Hot Dry 0.74
Fresno, CA East Hot, Dry Mixed Dry 0.49
Phoenix, AZ East Hot, Dry Hot Dry 0.13
Table 1: Moisture indices for the seven representative
cities chosen for parametric study.
1 4 • I N T E R F A C E O C T O B E R 2 0 0 4
no water ingress, there is little or no risk of
moisture-related damage. However, if water
ingress occurs, the general trend is clear.
The response of the wall to water ingress
increases non-linearly with increasing climate
severity (i.e., MI). Figure 3 suggests a
good fit between MImews and wall response
indicator. There is, however, an outlying
point shown in the figure. The explanation
of this anomaly rests with the nature of the
wall response measure and the temperature
regime of the climate in question – San
Diego. This is discussed in detail in the
summary findings of the MEWS project [3].
A partial explanation hinges on the interplay
of RH and T, whereby the hot-dry
climate of San Diego produces nearly the
same RHT as the mild-wet climate of Seattle.
In San Diego, the RHT accumulation is
contingent on occasional periods of high
RH, since the T threshold is always exceeded,
whereas in Seattle, the reverse is true.
The definition of MImews appears unable to
reveal the equivalence in terms of the RHT
criteria, but we should observe that a
change in materials (the middle curve) improves
drying and lowers RH to such an extent
that the anomaly disappears. This
underscores the difficulty of correlating hygrothermal
response of specific wall systems
with any MI that is independent of
construction details. However, that being
said, Figure 3 indicates that MI as a measure
of climate severity is directly related to
the risk of moisture-related damage, as it
should be.
APPLICATIONS OF MI
A Provisional Climate Zoning Map
Having established the Moisture Index
as a procedure for ranking climates, it is
possible to establish a method of grouping
like climates with respect to potential moisture-
related problems. Each grouping can
be shown as a zone on a map of North
America. Since the MI for a location is
defined as the distance that the location’s
climate WI, 1-DI coordinates lie from the
origin on a normalized plot (see Figure 2),
the boundary values for the groupings can
be expressed as radii.
Suppose a particular location has a normalized
Wetting Index, WInormalized, of one,
indicating maximum wetting potential, and
a normalized Drying Index, DInormalized, of one,
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Table 2: Proposed climate classification scheme used to make the provisional map.
Division Classification w.r.t. Moisture Problems Color
MI greater or equal to 1.0 Severe
MI greater or equal to 0.9 but less than 1.0 High
MI greater or equal to 0.8 but less than 0.9 Moderate
MI greater or equal to 0.7 but less than .0.8 Limited
MI less than 0.70 Low
indicating maximum drying potential. This
climate corresponds to the point (1, 0) on
the plot shown in Figure 2. Note that 1 –
DInormalized rather the DInormalized – is plotted on
the y-axis. This ranking corresponds to a
radius, r, equal to one. Similarly, a climate
having WInormalized = 0, minimum wetting, and
DInormalized = 0, minimum drying, corresponds
to the point (0, 1) in Figure 2. This climate
also lies on the arc r = 1. Although both
these climates might differ in terms of wetting
(rainfall) and drying (difference in
humidity ratios) characteristics, the hypothesis
is that they are similar with respect
to the potential for moisture-related problems.
Using an analogy to Mohr’s circle,
the climates represented
by points along a
radius are hypothesized to have an equal
(iso-) potential for moisture related problems.
A simple classification can be constructed
by splitting the range of MI into a
number of divisions. Each division represents
a limit for moisture-related problems.
Climates are then grouped accordingly. A
possible climate classification is given in
Table 2.
Figure 4 was constructed using 383 stations
reporting hourly data. The rankings
for each station were calculated using longterm
data, temperature, RH, and rainfall,
obtained from climate normals. The current
climate normals span the years 1961 to
1990. The Wetting Index was defined, as
before, as the annual average rainfall. The
Drying Index was computed using the
method described except that the average
annual temperature and average annual
relative humidity were used instead of
hourly values. A method to determine MI
from climate data was developed and
reported on by Cornick [10]. The method
makes use of average annual values to
reduce the calculation effort; the results
correlate well with those of the hourly
method.
A few comments on the provisional contour
map are worth mentioning. First, in
generating a contour map, a certain amount
of information is lost. Second, the network
of reporting stations used to generate
the map is sparse in the northern
regions of the continent. Third,
the selection of the MI
O C T O B E R 2 0 0 4 IN T E R F A C E •
Figure 4: A climate zone map for Canada and the USA.
defining limits to various climates regions is
not related to experimentally observed data,
but rather anecdotal data (e.g., real experience).
Application of the Methodology to Local and
Micro Climates
The Moisture Index methodology was
developed on a macroclimate scale. Hourly
and climate normal data (generally from
reporting stations at or near airports) were
used in the development and application.
Local and meso-climates can have a marked
effect, however, on the values of MI. The
west coast of North America features many
examples of local climates that vary
markedly over short distances. The Vancouver,
Seattle, and San Francisco Bay
areas are notable examples. These local climates
feature a small coastal littoral
backed by mountains and a cold
ocean current. Orographic lifting
of air on the windward side of
the coastal mountains
causes increased precipitation
with increased elevation on the
windward slopes and a rain shadow forms
on the leeward sides of the coastal mountains.
The MI value for San Francisco, for
example is 0.86, in the moderate category
defined in Table 2. Is this representative of
the San Francisco Bay area? The answer is
yes and no.
The MI methodology can be applied to
local as well as macro-climates. Like maps
showing elevation contours, the scale of the
analysis and mapping needs to be adjusted
to suit the purpose. If enough data are
available, then small-scale studies can be
done. The Bay Area, for example, has at
least 26 stations reporting temperature and
rainfall. The variation in annual average
temperature is around 3.3ºC. Although this
might not seem like much, the difference in
average annual temperature between
Vancouver, BC and Ottawa, ON (two distinctly
different climates) is only 4ºC. The
annual range reveals more, however. The
annual range for the Bay Area ranges from
5ºC to 14ºC. The mean range of the reporting
stations in the Bay Area is about 10ºC,
while the annual ranges for Vancouver and
Ottawa are 14ºC and 32ºC respectively.
Temperature in the Bay Area is not the
determining factor for calculating MI.
Similarly, the variation in relative humidity
is not significant with respect to the Drying
Index. The Drying Index in and around San
Francisco ranges from 0.15 to 0.19 when
normalized (divided by the value for
Phoenix of 124.6). The variation in rainfall
in the Bay Area, however, paints a different
picture. Climate normal data from the Bay
Area reporting stations show a range in
average rainfall of about 880 mm.
Applying the MI methodology to the San
Francisco Bay Area using the annual data
provided by the local reporting stations,
shows most of the stations are in the same
risk category as the airport reporting station.
Two stations (#3 San Rafael Civic
Center and #21 San Gregorio 2 SE), however,
are promoted into the high-risk category,
and one station into the severe risk
category (#2 Kentfield). A map of the Bay
Area is shown in Figure 5. Airport data are
generally representative of large areas and
useful for large-scale studies. However, in
an area where considerable variation is
known to occur (especially in rainfall), airport
data are not appropriate. Fortunately,
the MI method can be easily applied on a
local scale if sufficient data are available or
reasonable approximations can be made.
Selecting Moisture Reference Years
The International Energy Agency (IEA)
Annex 24 on heat, air, and moisture transport,
Task 2 Environmental Conditions, has
made recommendations on how to determine
a moisture design year [12]. Some of
the methods require the use of specific
building and wall characteristics. The
approach taken in the MEWS project was
that the climate data would be analyzed
independently of the wall response.
Consequently, many of the IEA recommendations
did not serve the purposes of this
project. The approach taken to selecting
weather for hygrothermal modeling was to
construct input files spanning three years
using actual weather data. Using the
Moisture Index, it is possible to classify
individual years as “wet,” “dry,” or “average.”
Figure 5: MI values for 26 stations in the San Francisco Bay area. The airport is labeled 15.
1 8 • I N T E R F A C E O C T O B E R 2 0 0 4
For a particular city, the Moisture Index
for each year was calculated, the hypothesis
being that the higher the Moisture Index,
the greater the potential for moisture loading.
“Wet” and “dry” years were defined as
those years that deviate more than one
standard deviation from the mean MI value
of the sample set for a city. “Average” years
were defined as being within one standard
deviation of the mean. The “wet” year for a
city was defined as the year with the highest
Moisture Index, the “dry” year as the
year with the lowest Moisture Index, and
the “average” year as the year closest to the
mean Moisture Index.
Figure 6 shows three years selected as
“wet,” “dry,” and “average” for Wilmington,
North Carolina. The chart shows the deviation
of the Moisture, Drying, and Wetting
indices from the mean in terms of standard
deviations, σ. Years selected as “wet,” “dry,”
and “average” are highlighted. The dry year
can be seen to have a higher than normal
Drying Index and a lower than normal
Wetting Index. The combination produces
the lowest Moisture Index. The wet year is a
combination of low DI and high WI producing
the highest value of MI.
Average years lie close
to the mean MI.
ORIENTATION AND PREDOMINATE DIRECTION
Up to this point, the Drying Index and
wetting indices have been developed without
considering building orientation. This
was in keeping with the a priori decision
that climate would be treated independently
of the wall or building. Recall that the
Wetting Index was defined as the annual
rainfall on the horizontal. The scope of the
MEWS parametric study phase, however,
was limited to analyzing one wall orientation.
This required a modification of WI.
Why?
Figure 7a shows directional driving rain
indices (dDRI) for two “wet” years, an “average
year,” and a “dry” year, selected from
the Wilmington, NC weather record. In the
Moisture Index used for selection, WI was
equal to the annual rainfall on the horizontal.
Suppose that the orientation of a given
wall is south. The hygrothermal model will
impose a rain load on the wall in proportion
to the wind speed, wind direction, and rain
intensity. A south-facing wall will see more
rain during the “average” year than during
both “wet” years. If one wished to compare
the wall response to the “wet” year 1989
with the dry year 1968, a north or northeast
orientation would be preferable.
Clearly, WI must take direction into
account if only one wall orientation were to
Figure 6: A plot showing the deviations of WI and DI for individual years from the mean.
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be considered. To include the effect of orientation
on wind-driven rain, a modified
Wetting Index was based on a method recommended
by Straube [13][10]. The first
step in introducing a directional component
was to determine the predominant direction
of rainfall as it relates to wind speed and
direction. The rain impinging on the wall
was calculated for all the years available.
The rain load on the wall was calculated for
the four cardinal orientations for each city.
The direction with highest amount of total
rain impinging on the wall was selected as
the predominant direction for rainfall.
Instead of using the rainfall for the year as
the wetting component for that year’s MI,
the wetting component is now calculated as
the amount of water impinging on a wall in
the predominant direction. The years
selected for the hygrothermal model as
“wet,” “dry,” and “average” for Wilmington,
NC are shown in Figure 7b. Note that the
selection of the Moisture Reference Years
when compared with those shown in Figure
7a now show a bias towards wetting in the
direction of predominate rainfall.
CONCLUDING REMARKS
For the purposes of characterizing moisture-
related problems in building
envelopes, climate can be described by a
Moisture Index that combines two independent
indices, a Wetting Index (rainfall), and
a Drying Index (potential evaporation). The
MI can then be used to rank weather stations
in a climate classification scheme.
Increasing concerns for adequate moisturerelated
performance of wall cladding systems
have heightened interest in
hygrothermal models. This, in turn, drives
the need for appropriate Moisture Reference
Years to be used as input for model studies.
To select appropriate MRYs, it is desirable
to classify weather years according to criteria
relevant for the problem at hand. As just
one example, sequences of years can be
assembled to deal with problems such as
long-term performance or limit-state design
– i.e., recurrence of years that severely
stress the wall assembly. There is probably
no one definitive set of MRYs that is appropriate
to solve all the hygrothermal problems
of interest. Similarly, there exists no
definitive method for selecting MRYs.
Different sets of MRYs should be produced
to suit different problems.
Figure 7a: Four years classified as “wet,” “average,” and “dry” using rainfall as the WI.
Figure 7b: Three years classified as “wet,” “average,” and “dry” using
directional driving-rain as the WI.
2 0 • I N T E R F A C E O C T O B E R 2 0 0 4
The MEWS Moisture Index offers several desirable features for
hygrothermal modeling:
1) It characterizes years statistically, e.g., to select sequences
of years for climate input.
2) Wetting and drying functions can be tailored for specific
problems of interest as can the relationship between wetting
and drying.
3) MI is quick and easy to implement and calculate, given adequate
climate data.
The provisional map showing five climate zones of MI, labelled
“low” to “severe,” should be viewed with caution. Local areas with
rapid changes in MI will require special treatment on a smaller
scale, and more importantly, MI alone should be considered as only
an initial warning of potential moisture-related problems in building
envelopes. MI as defined occasionally fails to rank the
hygrothermal responses of certain wall systems correctly according
to climate. It is unlikely that any construction-independent MI will
escape the necessity of confirmation by hygrothermal modelling or
case studies of actual wall systems. Finally, confidence in
hygrothermal modeling itself depends on validation by wellcontrolled
laboratory experiments, such as those done by MEWS,
as well as well-documented field experiments.
REFERENCES
1) Canada Mortgage and Housing Corporation, Survey of
Building Envelope Failures in the Coastal Climate of British
Columbia, 1996.
2) Chouinard, K. L., and M. D. Lawton, “Rotting Wood Framed
Apartments – Not Just a Vancouver Problem,” Proceedings of
the Eighth Conference on Building Science and Technology,
Toronto, Canada, February 22-23, 2001. pp. 304-318.
3) Beaulieu, P.; Bomberg, M.; Cornick, S.; Dalgliesh, A.;
Desmarais, G.; Djebbar, R.; Kumaran, K.; Lacasse, M.;
Lackey, J.; Maref, W.; Mukhopadhyaya, P.; Nofal, M.;
Normandin, N.; Nicholls, M.; O’Connor, T.; Quirt, J.;
Rousseau, M.; Said, M.; Swinton, M.; Tariku, F.; van
Reenen, D., Final Report from Task 8 of MEWS Project (T8-03)
– Hygrothermal Response of Exterior Wall Systems to Climate
Loading: Methodology and Interpretation of Results for
Stucco, EIFS, Masonry and Siding Clad Wood-Frame Walls
(IRC-RR-118), 2002.*
4) Djebbar, R.; Kumaran, M.K.; Van Reenen, D.; Tariku, F.
“Use of Hygrothermal Numerical Modelling to Identify
Optimal Retrofit Options for High-rise Buildings,” 12th
International Heat Transfer Conference, Grenoble, France,
Aug, 2002, pp. 1-6, (NRCC-45215).*
5) Lstiburek, J. W., “Hygrothermal Climate Regions, Interior
Climate Classes, and Durability,” Proceedings of the Eighth
Conference on Building Science and Technology, Toronto,
Canada, February 22-23, 2001. pp. 319-329.
6) Russo, J. A., The Complete Money-Saving Guide To Weather
For Contractors, Environmental Information Services
Associates, Connecticut, USA, 1971. pp. 78-79.
7) Boyd, D. W., Driving Rain Map of Canada, Technical Note
398, Division of Building Research, National Research
Council of Canada, Ottawa, 1963.
O C T O B E R 2 0 0 4 IN T E R F A C E •
8) Setliff, E. C., “Wood Decay Hazard in
Canada Based on Scheffer’s Climate
Index Formula,” The Forestry
Chronicle, October 1986: 456-459.
9) Bailey, H. P., “A Simple Moisture
Index Based Upon a Primary Law of
Evaporation,” Geog. Ann., 1958, 40:
196-215.
10) Cornick, S. M., Dalgliesh, W. A.,
Said, N. M., Djebbar, R., Tariku, F.,
Kumaran, M. K Report from Task 4
of MEWS – Environmental Conditions
Final Report, Institute for Research
in Construction, National Research
Council of Canada, IRC-RR-1130,
2002.*
11) Hagentoft, C. E., Harderup, E.,
“Climatic Influences on the Building
Envelope Using the Π Factor,” IEAAnnex
24 Hamtie Task 2,
Environmental Conditions. Closing
Seminar, Finland, 1996.
12) Sanders, C., “Environmental Conditions,
Final Report. Task 2.”
International Energy Agency. Energy
Conservation in Buildings and
Community Systems, Annex 24
Heat-Air and Moisture Transfer in
Insulated Envelope Parts (HAMTIE).
Laboratorium Bouwfysica, K.U.-
Leuven, Belgium, 1996.
13) Straube, J. F., Moisture Control and
Enclosure Wall Systems, Ph.D.
Thesis, Civil Engineering Department,
University of Waterloo, 1998.
* Full text at http://www.nrc.ca/
irc/publications.html.
Editor’s Note: A version of this document is
published in the Proceedings of the 9th
Canadian Conference on Building Science
and Technology, Vancouver, B.C., Feb. 27-
28, 2003, pp. 383-398. It was also presented
as a part of the 2003 RCI Building Envelope
Symposium, Nov. 6-7, 2003 in Dallas, Texas.
Reprinted with permission.
MEWS is a joint research project between
IRC-NRC Canada and several external
partners. More information about the MEWS
project can be obtained from the Institute for
Research in Construction.
Steven M. Cornick is a research officer for the National
Research Council of Canada’s Institute for Research in
Construction. He has worked for the last 18 years in the
Building Envelope and Structure Program. For the past six
years, Cornick’s focus has been on environmental factors and
methods characterizing the wetting and drying potentials of
the exterior climate and long-term performance of wall
cladding systems. As an engineer, Cornick uses his knowledge
of laboratory testing protocols to find answers to complex
design issues. He sits on ASHRAE’s Technical Committee 4.2, “Weather
Information for Buildings.” Cornick is currently working on a hygrothermal numerical
model to simulate the movement of heat, air, and moisture through building envelopes.
Steven M. Cornick
W. Alan Dalgliesh is a consultant and former research officer
at the Institute for Research in Construction, National
Research Council of Canada. Dalgliesh, an expert on highrise
buildings and wind effects on buildings, has written or
co-authored approximately 90 publications. He is a member
of the Association of Professional Engineers, Geologists, and
Geophysicists of Alberta, Alberta Building Envelope Council
South, Canadian Society for Civil Engineering, and Canadian
Standards Association’s Strategic Steering Committee on
Structures. Alan has a bachelor’s degree in civil engineering from the University of
Alberta and his masters in structural engineering from Carleton University.
W. Alan Dalgliesh
2 2 • I N T E R F A C E O C T O B E R 2 0 0 4
Architect/Engineer, Building Envelope Consultant: Quality-oriented
building envelope consulting firm in Seattle is seeking a licensed Architect or Engineer
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required. Position entails conducting field surveys, providing project coordination, preparation
of detailed evaluation and inspection reports, along with specification and drawing
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lkelly@bet-r.com.
Residential construction in the U.S. showed a
20% increase in the first six months of 2004,
accounting for 57% of all construction during that
period, according to McGraw-Hill Construction. This
allowed for a 10% increase over construction for the
same period in 2003, it was reported. The nonresidential
market was down 1% from 2003. — ENR
Construction Growth
Carried by Housing