Tree Physiology 27, 561–575
© 2007 Heron Publishing—Victoria, Canada
Nighttime transpiration in woody plants from contrasting ecosystems
TODD E. DAWSON,1,2,3 STEPHEN S.O. BURGESS,4 KEVIN P. TU,1 RAFAEL S. OLIVEIRA,1,5
LOUIS S. SANTIAGO,1,6 JOSHUA B. FISHER,3,7 KEVIN A. SIMONIN1 and ANTHONY
R. AMBROSE1
1
Department of Integrative Biology, Valley Life Sciences Building, University of California, Berkeley, CA 94720, USA
2
Corresponding author (tdawson@berkeley.edu)
3
Department of Environmental Science, Policy & Management, Mulford Hall, University of California, Berkeley, CA 94720, USA
4
School of Plant Biology, University of Western Australia, 35 Stirling Highway, Nedlands, WA 6009, Australia
5
Lab. Ecologia Isotópica - CENA, Universidade de São Paulo, Av. Centenário, 303, 13.416-000, Piracicaba, SP, Brazil
6
Present address: Department of Botany & Plant Sciences, 2150 Batchelor Hall, University of California, Riverside, CA 92521,USA
7
Present address: Oxford University Centre for the Environment, South Parks Road, Oxford, OX1 0EZ, U.K.
Received June 27, 2006; accepted October 19, 2006; published online January 2, 2007
able (in wet soils) and transport is rapid; (3) it may allow for the
delivery of dissolved O2 via the parenchyma to woody tissue
sinks; or (4) it may occur simply because of leaky cuticles in
older leaves or when stomata cannot close fully because of obstructions from stomatal (waxy) plugs, leaf endophytes or
asymmetrical guard cells (all non-adaptive reasons). We discuss the methodological, ecophysiological, and theoretical implications of the occurrence of En or gn for investigations at a
variety of scales.
Keywords: nighttime stomatal conductance, porometry, sap
flow, water balance, water relations, woody plants.
Introduction
“. . . there is much contradictory evidence as to whether or
not the stomata of the majority of plants close at night.”
Francis Darwin (1898)
A longstanding notion among plant physiologists, which is
captured by Francis Darwin's comment, is that C3 plants close
their stomata in the dark (see also Meidner and Mansfield
1965, and citations in Kramer and Boyer 1995 and Nobel
1999). Despite evidence to the contrary, this concept has persisted since the earliest observations of stomatal behavior
(Leitgeb 1886, Darwin 1898). Over 100 years ago Darwin
(1898) estimated that 87% of terrestrial plants open their
stomata at night, with values for wetland and aquatic species
approaching 100%. Nevertheless, the assumption that stomata
close in the dark (at night) is consistent with the nearly universal observation that stomatal conductance in daylight is at its
highest over a diel cycle (Kramer and Boyer 1995, Richie
1974). Furthermore, a range of studies have shown that the
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Summary It is commonly assumed that transpiration does
not occur at night because leaf stomata are closed in the dark.
We tested this assumption across a diversity of ecosystems and
woody plant species by various methods to explore the circumstances when this assumption is false. Our primary goals were:
(1) to evaluate the nature and magnitude of nighttime transpiration, En, or stomatal conductance, gn; and (2) to seek potential
generalizations about where and when it occurs. Sap-flow,
porometry and stable isotope tracer measurements were made
on 18 tree and eight shrub species from seven ecosystem types.
Coupled with environmental data, our findings revealed that
most of these species transpired at night. For some species and
circumstances, nighttime leaf water loss constituted a significant fraction of total daily water use. Our evidence shows that
En or gn can occur in all but one shrub species across the systems we investigated. However, under conditions of high nighttime evaporative demand or low soil water availability, stomata
were closed and En or gn approached zero in eleven tree and
seven shrub species. When soil water was available, En or gn
was measurable in these same species demonstrating plasticity
for En or gn. We detected En or gn in both trees and shrubs, and
values were highest in plants from sites with higher soil water
contents and in plants from ecosystems that were less prone to
atmospheric or soil water deficits. Irrespective of plant or ecosystem type, many species showed En or gn when soil water deficits were slight or non-existent, or immediately after rainfall
events that followed a period of soil water deficit. The strongest
relationship was between En or gn and warm, low humidity and
(or) windy (> 0.8 m s – 1 ) nights when the vapor pressure deficit
remained high (> 0.2 kPa in wet sites, > 0.7 kPa in dry sites).
Why En or gn occurs likely varies with species and ecosystem
type; however, our data support four plausible explanations:
(1) it may facilitate carbon fixation earlier in the day because
stomata are already open; (2) it may enhance nutrient supply to
distal parts of the crown when these nutrients are most avail-
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DAWSON ET AL.
assume no water flux occurs through plants at night (Iritz and
Lindroth 1994, Green et al. 1989, Vertessy et al. 1997, but see
Fisher et al. 2007). If this assumption is incorrect then models
assuming that evapotranspiration at night is zero (Iritz and
Lindroth 1994, Benyon 1999) will underestimate fluxes and
incorrectly assess site water balance (see Fisher et al. 2007).
Here, we present data demonstrating that nighttime transpiration (En) and nighttime stomatal conductance to water vapor
(gn) are widespread among a range of tree and shrub species
inhabiting a broad range of environments. For some species
that show En or gn, nocturnal water loss can represent a significant fraction of the total daily water used and therefore of total
ecosystem water loss. We present selected examples and,
based on these and a broader review of the literature, discuss
the patterns emerging from these observations and the implications for ongoing and future water relations investigations at
scales ranging from the individual plant to whole catchments.
We conclude that our findings have important implications for
the selection of appropriate sap-flow methods (e.g., the compensation heat pulse method is a poor choice if quantitative assessments of En are desired) and for an established body of water relations theory that assumes water loss from leaves at
night does not occur.
Materials and methods
Study sites and species
Our investigations were carried out at 10 study sites (Table 1)
representing six biomes on three continents, plus the Hawaiian
Islands (see Table 2). Our goal in choosing sites and species
was to measure sufficient diversity to assess the occurrence of
En or gn, or both, in phylogenetically divergent woody plants
exposed to different site conditions.
Our studies of En based on the heat ratio sap-flow method
(HRM; see the methods section that follows) in the coniferous
coastal redwood ecosystem were carried out at two locations
in coastal California as previously described by Burgess and
Dawson (2004). The following tree and shrub species were
studied: Sequoia sempervirens Lamb. ex D. Don (coast redwood), Pseudotsuga menziesii (Mirb.) Franco. (Douglas-fir),
Lithocarpus densiflora (Hook. and Arn.) Rehd. (tanbark oak)
and Umbellularia californica Nutt. (California bay-laurel).
The redwood trees examined were canopy dominants, whereas
the other species were mature sub-dominants growing in open
forest gaps and were not shaded by larger neighbors. One
understory shrub species, Gaultheria shallon Pursh (salal) at
two of these sites was also studied by a porometric method.
Measurements of nighttime stomatal conductance (gn) and
water flux in Acer saccharum Marsh. (sugar maple) trees in a
Northern Hemisphere temperate deciduous forest were measured by porometric and deuterium isotope-tracer methods as
described previously (Dawson 1996, Pausch et al. 2000). Acer
rubrum L. (red maple) trees were measured about 2 km west of
this site on an exposed ridgeline on rocky, well-drained soils.
This site was windier and experienced 10–15% lower relative
humidity than the A. saccharum site. At the A. rubrum site, we
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ionic balance (mostly K+ and Cl – flux) and the abscisic acid
concentration in the guard cell complex can change over the
day–night period and that these changes are associated with
changes in guard cell turgor pressure that are known to elicit
closure when light is largely absent (Buckley 2005). Important
exceptions to this pattern were reported in trees over 30 years
ago (Hinckley and Scott 1971, Hinckley and Ritchie 1973), as
well as more recently in other woody plants (Donovan et al.
2000, 2003) and a variety of herbaceous species (Muchow et
al. 1980, Snyder et al. 2003). Yet, despite this evidence, the
predominant view advocated in most biology and even plant
physiology textbooks describing stomatal function is that the
stomata of leaves of non-CAM plants are closed in the dark. It
follows therefore that most studies of water balance at the
whole-plant-, ecosystem- and catchment-scales have assumed
nocturnal transpiration to be zero.
Recent advances in sap flow methods (see Burgess et al.
2001a) have facilitated precise and continuous measurement
of plant water use over day–night cycles. Using such methods
(and others), a growing number of studies, including those presented here, have revealed previously unknown patterns of
nighttime water flux and loss from plant crowns across a variety of woody taxa (Burgess et al. 1998, Hultine et al. 2004,
Burgess and Dawson 2004, Bucci et al. 2004, Oliveira et al.
2005a). As we prepared this publication at least 20 studies, not
including papers in this issue of Tree Physiology, have reported a continued flux of water into plants at night, well after
stomata were assumed to be closed (e.g., Becker 1998, Benyon
1999, Iritz and Lindroth 1994, Hogg and Hurdle 1997,
Gutiérrez and Santiago 2006, Green et al. 1989, Oren et al.
1999, Donovan et al. 1999, 2001, 2003, Snyder et al. 2003,
Grulke et al. 2004). Many of these same studies also show water loss from leaves at night. Nighttime water flux in stems and
leaves occurs because leaf water potential declines over the
course of daytime transpiration to the point that, when transpiration ceases, a water potential gradient between leaf and soil
remains (Hinckley 1971). This water potential gradient drives
water movement that can be detected by sap flow sensors (see
Burgess and Dawson 2004). Until recently, much of this flux
was attributed to refilling of partially depleted xylem water
stores that were exhausted during daylight hours by plant transpiration (Oren et al. 1999). However, further analysis of
sap-flow behavior based on improved methods, which allow
detection of very low sap-flow rates in the xylem (e.g., Burgess and Dawson 2004, Burgess et al. 1998, 2001b, Hultine et
al. 2004, Brooks et al. 2002, Oliveira et al. 2005a), have
shown that a significant fraction of the sap flow that occurs at
night is not limited to the refilling of depleted xylem water
stores. These and many previous results based on other methods (e.g., Hinckley and Ritchie 1973) suggest that many plants
transpire at night.
Incomplete closure of stomata at night with continued transpirational water loss has important implications for some of
the commonly used methods in plant water relations research
as well as some long-standing theories in plant science (Donovan et al. 1999, 2001, 2003, Bucci et al. 2004). In addition,
many plant-, stand- and catchment-based models of water flux
NIGHTTIME TRANSPIRATION IN WOODY PLANTS
563
Table 1. Summary of study site characteristics and the species examined. Abbreviations: MAP, mean annual precipitation; and MAT, mean annual
temperature.
Country
Ecosystem type
Latitude, Longitude
MAP (mm) MAT (°C)
Species examined
Sonoma
USA
Coastal temperate
coniferous forest
38°24′ N, 122°59′ W
1037
15
Sequoia sempervirens
Pseudotsuga menziesii
Lithocarpus densiflora
Umbellularia californica
Gaultheria shallon
Big Basin
USA
Coastal temperate
coniferous forest
37°10′ N, 122°14′ W
995
17
Sequoia sempervirens
Pseudotsuga menziesii
Lithocarpus densiflora
Umbellularia californica
Gaultheria shallon
Upstate New York USA
Temperate deciduous forest
42°21′ N, 76°24′ W
1470
19
Acer saccharum
Acer rubrum
Pinus strobus
Vaccinium spp.
Blodgett Forest
USA
Montane temperate
coniferous forest
38°53′ N, 120°37′ W
1290
12
Pinus ponderosa
Arctostaphylos manzanita
Ceanothus cordulatus
Tonzi Ranch
USA
Mediterranean oak savannachaparral
38°25′ N, 120°57′ W
560
16
Quercus douglasii
Bolinas Ridge
USA
Mediterranean oak savannachaparral
37°54′ N, 122°37′ W
1250
12
Quercus agrifolia
Lithocarpus densiflora
Arctostaphylos glandulosa
Ceanothus cuneatus
Rhamnus californica
Heteromeles arbutifolia
Waikamoi
USA
Tropical montane forest
20°48′ N, 156°13′ W
5000
16
Metrosideros polymorpha
IBGE-RECOR
Brazil
Neotropical savanna
15°56′ S, 47°53′ W
1450
21
Byrsonima verbascifolia
Roupala montana
Vellozia flavicans
Floresta Nacional Brazil
do Tapajós
Tropical evergreen forest
2°26′ S, 54°42′ W
2000
25
Coussarea racemosa
Protium robustum
Manilkara huberi
Corrigin Water
Reserve
Mediterranean woodlands
and shrublands
32°19′ S, 117°52′ E
376
17
Allocasuarina campestris
Dryandra cirsioides
Isopogon gardneri
Hakea subsulcata
Banksia sphaerocarpa
Actinostrobus arenarius
Eucalyptus salmonophloia
Eucalyptus albida
Dryandra sessilis
Nuytsia floribunda
Eucalyptus wandoo
Australia
measured gn on open-grown Pinus strobus L. (eastern white
pine) saplings ranging in height from 8.2 to 11.6 m as well as
on two 1–2 m tall shrubs of Vaccinium spp. (blueberry). Mean
precipitation for these sites was 1470 mm annually, 57% of
which falls as snow, with a mean growing season temperature
of 19 °C (Table 1).
We used the HRM to measure sap flow at two other inland
sites: a mid-elevation coniferous forest in the Sierra Nevada
Mountains (California) dominated by Pinus ponderosa Dougl
ex P. Laws. (ponderosa pine) and two woody shrubs, Arctostaphylos manzanita Parry (manzanita) and Ceanothus cordulatus Kellogg (buckbrush), and an oak–savanna site on the east
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Site
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species throughout the semiarid region of southwestern Australia. Rudimentary measurements of En were also made on six
shrub and three tree species (Table 1) at this site.
Sap-flow methods and measurements
For most investigations we used the HRM (Burgess et al.
1998, 2001a, 2001b, Bleby et al. 2004, Oliveira et al. 2005a;
see also Smith and Allen 1996) to make continuous measurements of sap flow in stems of the target species. This wholeplant technique was chosen because it allows bi-directional
measurements of sap flow and also measures low flow rates
with high precision. Corrections for misalignment of the
probes were made according to Burgess et al. (2001a), but otherwise raw heat pulse velocities were used as a proxy for En. At
the end of all of our investigations, cuts were made into the
sapwood above and below the probes to stop sap flow, following the procedure suggested by Burgess et al. (2001a); this being the most accurate way to determine the reference velocity
(zero) flow value. Once this zero flow value was determined,
we were able to distinguish between true zero flow and the
small rates of flow that are associated with En. For ease of
comparison, we present En as percent of daily growing season
maximum E so as to account for differences in absolute flow
rates among species and individuals.
In California, at the montane temperate coniferous forest
site (Blodgett Forest, Table 1), HRM probes were placed in
five P. ponderosa trees, three A. manzanita and two C. cordulatus shrubs. Diameter at breast height (DBH) values for the
P. ponderosa trees were 18, 20, 21, 24 and 24 cm. At the Mediterranean oak savanna site (Tonzi Ranch; Table 1), we measured sap flow by HRM in five Q. douglasii trees. Values of
DBH for the Q. douglasii trees were 16, 18, 22, 23 and 37 cm
(see also Fisher et al. 2007). Three individuals of each of the
other species were investigated in the coastal temperate coniferous forest of sites (Sonoma and Big Basin, Table 1) as described in Burgess and Dawson (2004). Tanbark oak, a widespread species in the California flora, was also measured by
both sap flow and porometry at our Mediterranean site (Bolinas Ridge, Table 1).
At our tropical montane forest site in Waikamoi, Hawaii
(Table 1), transpiration was estimated as sap flow by the constant heating method (Granier 1985) during the months of
September 1996 to February 1997. Over this period, a total of
24 trees were measured in well-drained and waterlogged soils.
Because the constant heating method defines zero flow as the
lowest point measured during the night, nighttime transpiration was defined conservatively as visible peaks in nighttime
basal sap flow that coincided with VPD values that clearly rose
above zero. Although we cannot eliminate the possibility that
what we defined as zero flow for these measurements was not
a true zero (i.e., no flow), visible peaks in the nocturnal
sap-flow trace that occurred simultaneously with extremely
rare nighttime VPD values above zero were considered indicative of En, at least in this species, and thus represent a conservative qualitative estimate of En. In instances where Granier-type
probes are used and suggest the possible existence of En, we
recommend empirical verification of ∆Tmax values by cutting
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side of the great central valley of California dominated by the
hardwood tree species Quercus douglasii Hook and Arn. (blue
oak). Both sites were studied during the 2005 growing season
(cf. Fisher et al. 2007).
Species that inhabit the widespread chaparral vegetation of
California were studied at Bolinas Ridge, a near-coastal site
just north of San Francisco (as described by Kennedy and
Sousa 2006) that receives about 1250 mm of precipitation annually and has a mean annual temperature of 12 °C (Table 1).
This site also receives an additional 200–340 mm of “occult”
precipitation from coastal fog during the summer months. Two
tree species, Q. agrifolia Nee. (coast live oak) and L. densiflora (Hook. and Arn.) Rehd., and four shrub species, A. glandulosa ssp. glandulosa Eastw. (manzanita), C. cuneatus
(Hook.) Nutt. (buckbrush), Rhamnus californica Esch.
(coffeeberry) and Heteromeles arbutifolia M. Roem (toyon),
were measured by porometery during two one-week periods in
June 2000 and 2001.
In Hawaii, we investigated En in Metrosideros polymorpha
Gaud. (Ohia) at Waikamoi, Maui, a montane forest, by the
constant heating method, as described by Santiago et al.
(2000). The site has a mean annual precipitation of about
5000 mm, and a mean temperature of 16 °C (Table 1). Metrosideros polymorpha grows from sea level to treeline in Hawaii,
is the canopy dominant in most Hawaiian forests, and comprises 50–80% of basal area at the site. Soil waterlogging is
common at the site and many of the woody species exhibit
aboveground rooting (see Santiago et al. 2000).
Investigations in the neotropical savanna (Cerrado) were
made at the IBGE-RECOR ecological reserve in central
Brazil. Sap flow was measured by HRM on three common
species (Table 1) between 2001 and 2003. The 1350-ha IBGERECOR ecological reserve includes extensive areas of all major physiognomic forms of Cerrado vegetation. The most common structural type is Cerrado sensu stricto; a savanna woodland with abundant evergreen, deciduous and semi-deciduous
trees and shrubs, and a herbaceous understory with a semiclosed canopy with tree cover of about 50%. Mean annual
rainfall is 1450 mm with a very distinct 5-month dry period
(May–September). Less than 10% of total annual precipitation falls during this period, indicating a strong seasonality of
rainfall (see Oliveira et al. 2005b for additional details).
We studied three tropical evergreen forest trees species (Table 1) at the Floresta Nacional do Tapajós, located in east-central Amazônia (see Oliveira et al. 2005a). The forest is characterized as broadleaf evergreen located on a broad, flat plateau.
Mean annual rainfall is about 2000 mm with a distinct
3–5 month dry period (August-December). Less than 15% of
total annual precipitation falls during this period indicating
strong seasonality in rainfall. This forest can experience severe
drought during El Niño events, when annual rainfall can drop
to 800 mm.
Measurements at the southern hemisphere Mediterranean
woodland site were made at the Corrigin Water Reserve about
2 km west of Corrigin, Western Australia. We focused our
measurements of En on the dominant tree, Eucalyptus
salmonophloia F. Muell. (salmon gum), a widespread canopy
NIGHTTIME TRANSPIRATION IN WOODY PLANTS
Nighttime stomatal conductance
Measurements of stomatal conductance in daylight (g) and at
night (gn) were made with a steady state porometer (Model
LI-1600, Li-Cor, Lincoln, NE) on six trees each of Acer
saccharum and A. rubrum and five trees of Pinus strobus. We
measured outer-crown sun leaves in the mid-crown (~10 m
high) and lower crown (~2 m high). Because it is likely that
there would be interspecific variation in both the closure of
stomata in response to darkness or in the magnitude of gn, all of
our gas exchange measurements were made 3 h after the light
at the site decreased to below 2 µmol m – 2 s – 1 . We measured
the conditions inside an empty and a closed chamber just before each leaf measurement to be sure that the baseline atmospheric humidity was well matched to the conditions surrounding each leaf just before it was measured. When using
the LI-1600 to make an empty or a closed chamber measurement, the chamber was held beside the measurement leaf but
was either open to air, or it was closed with a plastic or Al-foil
“leaf” in the chamber, respectively. In most cases, these measurements were identical. In cases where condensation might
have formed, the plastic or Al-foil “leaf” value was higher,
with the difference representing freely evaporating water from
the surface and not gn. Under these circumstances the leaves
were not measured. Measured values obtained on leaves that
fell below ~10 mmol m – 2 s – 1 were considered to be below the
accuracy of the instrument (M. Barbour and T. Buckley,
Landcare, New Zealand, personal communication) and were
therefore excluded from the analyses.
Deuterium isotope tracers
During one dry period (July) in the 1994 growing season, six
A. saccharum trees at the temperate deciduous forest site (Upstate New York; Table 1) were selected to receive isotopically
enriched water; three trees were randomly assigned to one of
the two treatments below. All trees ranged between 21 to 24 m
in height. The hydrogen isotope composition is expressed in
delta notation (δD, see Dawson and Brooks 2001). Deep soil
water at the site (before irrigation) had a δD value of –57
± 4.9‰ (n = 86 over 4 years). The isotopically enriched water
had a δD value of 250 ± 3.2‰ (n = 16 over the experimental
and analysis period). This enriched water source was applied
in two ways: either injected directly into the stem 50 cm
above the soil surface using a modified intravenous-bag fitted with a hypodermic needle inserted into a small hole
drilled into the sapwood of each tree that was elevated above
the entry point to provide a slightly positive pressure (hydraulic head) to minimize embolism (modified from Calder
et al. 1986); or applied uniformly to the soil at a rate equivalent to a 3 mm rainfall event from the crown drip-line inward
to the base of the tree at 1800 h. Stems were sampled 2 h before the tracer application and then, every 3 h after, it was applied from 2100 h until 0900 h the following day. Stems and
leaves were also sampled 30 h after labeling. For the values
presented (see Table 3), daylight rates were determined in a
separate experiment. At each sampling period, terminal
shoots (n = 3 to 5) and leaves at two crown heights were sam-
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the xylem and excluding thermal gradients as a possible contribution (e.g., see Köstner et al. 1998).
At our southern hemisphere tropical forest site (Floresta
Nacional do Tapajós; Table 1), HRM probe sets were installed
in eight individuals of three species representing different
functional types (see Oliveira et al. 2005a): Coussarea racemosa A. Rich (Rubiaceae), the most common tree species in
the Tapajós forest, represented an understory type; Protium
robustum (Swart) Porter (Burseraceae), a mid-canopy species
and Manilkara huberi (Ducke) Stand. (Sapotaceae), representing a canopy species, also very common in this forest
(I. Tohver, University of Brazilia, personal communication).
At our neotropical savanna site (IBGE-RECOR; Table 1),
we selected nine individuals of three species that had contrasting leaf phenologies and were also common at the site (among
the 15 most frequent and abundant species; Lenza 2005).
Byrsonima verbascifolia L. (Malpighiaceae) is a brevideciduous tree, i.e., it is leafless for a short period of the end of the
dry season. It is common in the study area and ubiquitous
throughout the Cerrado (Ratter et al. 2003). Roupala montana
Aubl. (Proteaceae) is a tree of low stature (1–3 m) that remains
evergreen during both seasons but reduces its leaf area during
the dry season (Franco 1998). It is the most common species in
the study site (Lenza 2005) and also widespread throughout
the Cerrado, occurring in at least 50% of the 376 areas surveyed by Ratter et al. (2003). Vellozia flavicans is a desiccation-tolerant monocotyledonous shrub (Oliveira et al. 2005b).
It is common in the study site and occurs interspersed with the
other species. It can grow to 1.5 m and is a true evergreen,
maintaining constant leaf area throughout the year despite
changing conditions. We chose only mature individuals (of
similar sizes for each species) occurring within a randomly selected plot of 200 m2.
In Australia, at the Mediterranean woodlands and shrublands site (Corrigin Water Reserve; Table 1), sap flow was
measured in stems of 2–3 individuals of each species, with
two or three probes per tree, depending on tree size. Eucalyptus wandoo Blakely and E. salmonophloia F. Muell. are known
to exhibit nighttime sap flows up and down stem tissues owing
to hydraulic redistribution processes following rain (Burgess
and Bleby 2006). Consequently, data were selected from a
rainless period of sufficient duration that hydraulic redistribution processes could be assumed to be absent. Nighttime values were gathered between 2230 and 0430 h on numerous
summer nights. Because of ongoing experiments at this site, a
zero estimate by cutting xylem was made for only one probe
set in a single E. salmonophloea tree and only these data are
presented (see Figure 1). Values of En were normalized against
maximum daytime summer transpiration, which was calculated as the mean of three half-hourly measurements made between 1130 and 1230 h for five consecutive sunny midsummer
days (n = 15). For other species, zero estimates could not be
made because of ongoing measurements and so data were analyzed simply for correlations between nighttime sap flow (between 2230 and 0430 h) and VPD to provide an index of nighttime En. Data for E. salmonophloea were collected on 39
nights.
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DAWSON ET AL.
pled. The isotope data are shown as: (1) the percent difference
from the pretreatment (see Figure 8); and (2) rates of water
loss (for our case, En) calculated based on the tracer
counts/convective–dispersive equations outlined by Calder et
al. (1986), where changes in isotope concentration per unit
time and distance traveled are used to obtain a rate of transpiration. For accurate estimates, the method requires knowledge
of the cross-sectional area of conducting xylem, estimated as
described by Pausch et al. (2000), and assumes a given porosity. A concentration–time curve is obtained and from this
curve a flow velocity and rate are calculated. A full description
of the methods and the calculations for determining rates of
transpiration based on this approach is given by Calder et al.
(1986) and Calder (1992). All samples were collected in airtight vials and stored frozen until they were cryogenically extracted (see Ehleringer et al. 2000), and isotope analyses were
performed as outlined by Dawson (1996). Where noted, the
leaves directly adjacent to the sample stems were also measured at the same time with an LI-1600 porometer.
From the large amount of data we collected, only a few examples from a small number of the species are presented here to
illustrate particular patterns. These examples are representative of the responses that we observed in the wide variety of
tree and shrub species across the environments we studied. A
summary of the range of daylight and nighttime values we obtained from all of our studies is presented in Table 2.
Nighttime sap flow
Our California measurements spanned a longitudinal transect
across four ecosystems types: the coastal chaparral, the moist
coastal redwood forest, the dry oak and grass savanna of the
Central Valley, and the montane conifer-dominated forests of
the Sierra Nevada Mountains. Although these ecosystems experience contrasting microclimatic influences, they have similar timing of major wintertime storm events and seasonal
patterns of drought.
Burgess and Dawson (2004) found a strong positive correlation (r 2 = 0.84) between nighttime (0030 to 0530 h) sap flow
and VPD in Sequoia sempervirens growing in Sonoma
County, California. Nighttime rates of water loss exceeded
20% of maximum transpiration rate measured at noon under
warm and dry summer conditions. Nighttime transpiration
rates of 10 to 12% of summer maximum were common on dry,
often windy nights, but on some occasions, rates exceeding
40% of maximum were observed (when nighttime VPD exceeded 3.0 kPa and was associated with wind velocities of
0.8 m2 s – 1 ; data not shown). Several other species from this
temperate coniferous forest showed modest rates (6–11% of
daily maximum transpiration rates; Table 1) of En that were associated with VPD values in excess of 0.2 kPa (when relative
humidity dipped below 90%); in these cases there was also a
strong positive correlation between En and VPD for P. menziesii (r 2 = 0.71), L. densiflora (r 2 = 0.66) and U. californica
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Results
(r 2= 0.59) and between gn and VPD for the understory shrub
species, G. shallon (r 2 = 0.64). Our diurnal sap-flow traces indicate that little of the En we quantified was attributable to xylem refilling at the end of the day. For example, continuous
sap-flow traces obtained from three crown positions in S. sempervirens trees declined to near zero within 1 to 1.5 h after
dusk on high humidity nights, but declined quickly and then
remained at elevated flow rates on low humidity nights (see
Figure 2 of Burgess and Dawson 2004). This 1 to 1.5 h decay
in sap flow rate to a stable, non-zero value on low humidity
nights was observed in all of the tree species we investigated
and, we believe, represents xylem storage tissue recharge (data
not shown).
Fisher et al. (2007) reported similar coefficients of determination between VPD and nocturnal sap flow for Q. douglasii
(r 2 = 0.79) at the oak-savanna site and P. ponderosa (r 2 = 0.71)
in the Sierra Nevada Mountains. Nighttime transpiration as a
percentage of daily total transpiration was around 20% for
both sites and species. Nighttime water loss was minimal for
the Sierra Nevada understory shrubs, A. manzanita and
C. cordulatus.
In the Mediterranean Eucalyptus woodlands of the Southern
Hemisphere, we found a high correlation (r 2 = 0.69) between
VPD and En in E. salmonophloia (Figure 1). For the one probe
set for which a zero reference was made, rates of En were up to
18% of maximum daytime rates. Sap-flow traces from other
probe sets for which a zero reference was not obtained were
similar to those presented and broadly confirm the patterns
and flow rates we report. We also observed correlations between nighttime sap flow and VPD greater than 0.5 kPa in
E. wandoo (tree; r 2 = 0.69), Allocasuarina arenarius (shrub;
r 2 = 0.61) and Nuytsia floribunda (tree; r 2 = 0.53). Coefficients
of determination (r 2) of 0.45, 0.39, 0.34 and 0.32 were found
in E. albida Maiden and Blakely (tree), Dryandra sessilis R.
Br. (shrub), Isopogon gardneri Foreman (shrub) and Dryandra
sessilis (Knight) Domin var. sessilis (shrub), respectively,
whereas the remaining species (e.g., Hakea subsulcata Meisn.
(shrub), Banksia sphaerocarpa R. Br. var. sphaerocarpa
(shrub), Actinostrobus arenarius C.A. Gardner (tree) had
r 2 values ranging from 0.25 to near zero (S. Burgess et al., unpublished results). There was considerable variation among
individuals and the values reported are the strongest relationships we found; we consider them an index of the potential for
En.
The montane forest of Waikamoi, Hawaii typically experiences high humidities with nighttime VPDs near zero. In
M. polymorpha, we commonly observed a slow decline in
transpiration at the end of the day, reaching a steady rate that
was assumed to be zero approximately 2–4 h after sunset. We
consider the lag from sunset to this steady rate represents xylem storage tissue recharge. However, we also observed that,
after such recharge events, sap flow occasionally peaked again
in the dark and that these peaks coincided with non-zero VPD
(Figure 2). Nighttime peaks in sap flow were observed only at
times of non-zero VPD, supporting the interpretation that
nighttime peaks represent En. This qualitative indication of En
warrants further investigation with quantitative methods. Re-
NIGHTTIME TRANSPIRATION IN WOODY PLANTS
567
Table 2. Daytime and nighttime transpiration rates by ecosystem type, location and tree (t) and shrub (s) species. Data type is indicated in parenthesis as follows: transpiration, E, as sap velocity in cm h – 1 ; stomatal conductance, g, in mmol m – 2 s – 1 . Data daylight values, nighttime values and
the nighttime value as a proportion of the mean daylight value. Values at the higher end of each range are generally associated with summertime or
peak growing season maxima.
Biome
Type
Day
Coastal temperate and temperate deciduous and coniferous forests, USA
Acer saccharum (g)
t
130–355
Acer rubrum (g)
t
119–322
Pinus strobus (g)
t
52–222
Vaccinium spp. (g)
s
37–209
Sequoia sempervirens (E)
t
9–27
Pseudotsuga menziesii (E)
t
6–33
Lithocarpus densiflora (E/g)
t
11–40 / 82–195
Umbellularia californica (E/g)
t
23–31 / 52–178
Gaultheria shallon (g)
s
36–188
Pinus ponderosa (E)
t
1–19
Night
4.5–77
2.2–58
10.1–40
9.5–60
0.5–7.6
0.2–3.3
3.4–9.0 / 3.0–44
0–1.2 / 3.0–19
5.7–38.3
0–2
Night/Day
0.05–0.25
0.02–0.20
0.018–0.17
0.07–0.22
0.03–0.18
0.01–0.07
0.07–0.11
0.01–0.05
0.07–0.21
0–0.21
Mediterranean oak-savanna, USA
Quercus douglasii (E)
Arctostaphylos manzanita (E)
Ceanothus cordulatus (E)
t
s
s
Mediterranean chaparral, USA
Quercus agrifolia (g)
Lithocarpus densiflora (E/g)
Arctostaphylos glandulosa ssp. glandulosa (g)
Ceanothus cuneatus (g)
Rhamnus californica (g)
Heteromeles arbutifolia (g)
t
t
s
s
s
s
Tropical montane forest, Hawaii, USA
Metrosideros polymorpha (E)
t
0.3–1.8
0–0.3
0–0.18
Tropical evergreen forests, Brazil
Cousarea racemosa (E)
Manilkara huberi (E)
Protium robustum (E)
t
t
t
3–16
1–11
1–11
0–4.0
0–1.0
0–1.5
0.01–0.25
0.01–0.11
0.01–0.13
Neotropical savanna, Brazil
Byrsonima verbascifolia (E)
Roupala montana (E)
Vellozia flavicans (E)
t
t
s
0–30
2–35
0–18
0–3.5
0–5.0
0–2.0
0.01–0.12
0.01–0.14
0.01–0.11
2–8
0–1.5
0–0.18
gardless of whether the pattern is quantitative or not, this type
of response was observed in all three species studied and corresponded to the nighttime movement of dry air masses over
the islands, which is consistent with the assumption that the elevated basal sap flow was indicative of En. When air relative
humidity returned to near 100% and VPD was essentially zero
(between 0330 and 0600 h in Figure 2), sap flow continued,
presumably due to xylem refilling. Although absolute nighttime sap flow rates were low because of the high humidity in
this moist forest, nighttime sap flow constituted up to 17% of
mean maximum daily rates.
In the Amazon, we found a strong positive correlation between En and VPD in the tree species C. racemosa (r 2 = 0.54;
Figure 3). This was also observed in a tree common to the Brazilian Cerrado (savanna), B. verbascifolia (r 2 = 0.58; Fig-
15–183
8–34 / 39–147
22–244
48–326
33–190
21–277
0–3
0–1
0–1
0–9.5
1.9–3.6 / 1.0–22
2.5–23.8
0–0.6
12.4–40
0
0–0.18
0–0.06
0–0.07
0–0.02
0.03–0.08
0.05–0.15
0–0.01
0.03–0.08
0
ure 4). On average, En was about 57% of maximum daylight
dry season E for B. verbascifolia and about 12% for C. racemosa. As in S. sempervirens in California, rates of En approached between 10 and 30% of maximum transpiration rate
measured at midday during the hot dry season for both species.
Patterns of En in individual R. montana, V. flavicans (in
Oliveira et al. 2005b), M. huberi and P. robustum are consistent
with the patterns represented in Figures 3 and 4 (see also Table 2).
Nighttime stomatal conductance
As with our other study species, in two common maple tree
species of deciduous forest in northeastern USA, we found a
strong positive correlation (r 2 = 0.64) between nighttime sto-
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Mediterranean woodlands and shrublands, SW Australia
Eucalyptus salmonophloia (E)
t
1–20
0.5–16
0–15
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DAWSON ET AL.
matal conductance, gn and the leaf-to-air vapor pressure gradient, VPG (Figure 5). These direct measurements of water loss
from leaves were made at several different times of the growing season over a period of four years. Values were generally
higher in plants with low midday xylem pressure potentials
(< –0.9 MPa); data not shown, but see Figure 6). Overall, gn
was low, between 5 and 9% of daily maximum g, though on
dry (VPG > 1.6 kPa) nights it approached 25% of the mean
daily maximum g (Figure 5).
For maple trees, we commonly observed gn for up to 5 full
days (~120 h) following a significant (> 20 mm) summer rainfall event (Figure 6a), which also enhanced daylight g in both
A. saccharum and A. rubrum (Figure 7). When gn, g and their
ratio are plotted in relation to the number of days following
rainfall, we see a strong (r 2 = 0.92) negative correlation with
the highest values immediately following rainfall (Figure 7).
This relationship provides a strong and predictable index of
water loss from plants at night based on daylight values and
has important implications for modeling studies at the ecosystem and catchment scales.
tected within 3 h of application, maximum stem and leaf labeling was not observed until 12–15 h after application, or
between 0600 and 0900 h. Some of the highest accumulations
Nighttime transpiration estimated by deuterium labeling
experiments
The results of our deuterium labeling experiments are shown
in Table 3 and Figure 8 using both the stem base injection (Figure 8A) and soil irrigation (Figure 8B) treatments. Both treatments gave similar patterns, though isotope applied by direct
stem injection was detected sooner in both stem and leaf tissues (Figure 8A) compared with isotope applied in the soil irrigation treatment, reflecting the greater distance water applied to the soil must travel. Although the isotope could be de-
Figure 3. Relationship between vapor pressure deficit (VPD, kPa) and
nighttime transpiration (E n ) in Cousarea racemosa (in an Amazonian
forest) expressed as % of daylight maximum transpiration rate. Measurements were made between 2330 and 0530 h over 28 nights in the
dry season of 2001.
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Figure 1. Relationship between vapor pressure deficit (VPD, kPa) and
nighttime transpiration (En) in Eucalyptus salmonophloia expressed
as % of summertime maximum transpiration rate. Measurements
were made between 2230 and 0430 h over 39 summer nights in 2004.
Figure 2. Nighttime transpiration expressed as percent of maximum
daily sap flow for Metrosideros polymorpha from 2000 to 0600 h at
Waikamoi, Maui, Hawaii, in November 1996. The bar along the bottom of the figure shows the dark period. Sap flow at the stem base
rises in the night when relative humidity (RH; top panel) drops and
the vapor pressure deficit (VPD, kPa) rises (0000 to ~0300 h). The
slow decay of transpiration back to near zero from ~0300 to 0600 h is
likely to be xylem refilling.
NIGHTTIME TRANSPIRATION IN WOODY PLANTS
Figure 4. Relationship between vapor pressure deficit (VPD, kPa) and
nighttime transpiration (E n ) in Byrsonima verbascifolia expressed as
% of daylight maximum transpiration rate. Measurements were made
between 2330 and 0530 h over 14 nights in the dry season of 2001.
Figure 5. Relationship between the leaf-to-air vapor pressure gradient
(VPG, kPa) and nighttime stomatal conductance (gn) in sugar (Acer
saccharum, 䉬) and red (A. rubrum, 䉫) maple. Measurements were
made between 2300 and 0400 h over 77 nights during the 1994 to
1997 growing seasons.
Figure 6. Maximum rates of nighttime stomatal conductance in sugar
(Acer saccharum, 䉬) and red (A. rubrum, 䉫) maple species in response to the number of days since the last rainfall event. Measurements were made between 2300 and 0400 h on 30 different nights
during the 1994 to 1997 growing seasons.
between 15.1 and 6.6% of daily maximum values estimated
for the same trees (Table 3).
Discussion
Before discussing our findings, it is important to acknowledge
that a large fraction of the data that we and others have presented on En or gn were not originally collected with the primary goal of studying nighttime water loss. This highlights the
importance of analyzing data, particularly sap flow data, in relation to the solar period (daylight, night and total) or the occurrence of En could be overlooked. In the studies reported
here, En or gn was measured in every ecosystem type investigated and in both trees and shrubs, although the degree to
which En occurred, as indicated by the strength of the relationship between water flux and VPD or VPG, varied. For the species and ecosystems we investigated, En or gn generally occurred when nighttime VPD or VPG exceeded ~0.2 kPa for
plants inhabiting ecosystem types with high water availability
(e.g., at higher soil water contents or following rainfall events;
Figures 2–4) or, in the drought-prone ecosystems, when it was
slightly higher (~0.7 kPa) (Figures 1 and 5–7). In two cases,
En occurred when nighttime wind velocities exceeded 0.8 m
s – 1 (unpublished data). Taken together, the examples presented suggest that there are two drivers of En in the woody
plants we investigated: nighttime evaporative demand and soil
water availability. Furthermore, our data, as well as those presented previously (e.g., Darwin 1898, Hinckley and Scott
1971, Hinckley and Ritchie 1973, Rawson and Clarke 1988,
Matyssek et al. 1995, Assaf and Zieslin 1996, Donovan et al.
1999, 2000, Synder et al. 2003, Burgess and Dawson 2004 and
references therein) and in this collection of papers
(Cavender-Bares et al. 2007, Dawson et al. 2007, Fisher et al.
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of label occurred at 0900 h and were likely enhanced as a result
of stomatal conductance increasing in the early morning (after
0650 h on the day of observation) with increasing daylight.
The accumulation of isotope label with time in the dark suggests that water was being lost from leaves (cf. Calder 1992)
and this is corroborated by our porometric data (Table 2, Figures 5–7). Calculations based on the data shown in Figure 8
suggest that rates of water loss from leaves over an 8-h night
were between 0.0032 and 0.0014 m3 night – 1 (or 3.2 to 1.4l) or
569
570
DAWSON ET AL.
Figure 7. Daylight and nighttime
stomatal conductance in the two
maple tree species shown in Figures 5 and 6 in response to the
number of days since the last rainfall event. Measurements were
made between 2300 and 0400 h
during two 10-day/night periods
in the 1995 growing season. In the
upper right-hand corner the ratio
of these two measurements for
each day following rainfall is plotted. The regression shows that
there is a greater fraction of nighttime gn during the wettest periods
just following rainfall versus later.
Methodological implications
Our results have several important implications concerning
methods for investigating relationships between plants and
their water resources. For example, most, but not all, sap-flow
methods (e.g., HRM; after Marshall 1958) estimate canopy
water loss based on the assumption that nighttime water flux
through trees is zero. Some sap-flow methods not only assume
zero flow at night, but apply an algorithm that resets daily sen-
sor drift to zero each night (e.g., Granier 1985). Our objective
here is not to cast doubt on investigations that have used these
methods, particularly when used to estimate daylight transpiration, but to urge the need for care to insure the selection of an
appropriate method. If the objective is to document if, or
when, En occurs, the use of sensitive methods such as the
heat-ratio sap flow method (HRM; Burgess et al. 2001a) that
can resolve zero flow seems advantageous. Our data obtained
with the HRM show that, for woody plants inhabiting an array
of ecosystem types, nighttime transpiration occurs and therefore sap flow is rarely zero. Under conditions where En occurs
but zero flow is assumed, as is often the case with the Granier
(1985) method, the data obtained are qualitative at best and
therefore any conclusion drawn about the occurrence of En
needs verification. Our data for M. polymorpha (Figure 2), for
example, suggest the occurrence of En, but we believe a zero
estimate and verification that thermal gradients are not the
Table 3. Calculated rates of transpiration of Acer saccharum trees following deuterium tracer applications. Rates are estimated in m 3 day – 1 for
both daylight (E) and nighttime (En) periods for trees in the direct injection and soil application treatments. The first number is the rate for the upper (~20-m high) leaves and the second number is the rate for the lower (~5 m high) leaves. Rates of En were calculated from the data in Figure 8
and constructing an isotope concentration–time curve (after Calder 1986). Also shown are daylight (g) and nighttime (g n ) stomatal conductances
(mmol m – 2 s – 1 ), determined by porometery, for comparison with the values shown in Table 2.
Treatment
E
En
g
gn
Injected
Tree 1
Tree 2
Tree 3
0.0202, 0.0171
0.0303, 0.0194
0.0321, 0.0255
0.0022, 0.0015
0.0029, 0.0017
0.0014, 0.0015
244, 219
328, 309
277, 249
41, 32
29, 27
34, 30
Watered
Tree 1
Tree 2
Tree 3
0.0242, 0.0228
0.0309, 0.0265
0.0263, 0.0240
0.0023, 0.0020
0.0032, 0.0024
0.0027, 0.0025
259, 244
340, 318
292, 277
61, 36
70, 59
39, 32
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2007, Hubbart et al. 2007, Kavanagh et al. 2007, Marks and
Lechowicz 2007, Scholz et al. 2007, Seibt et al. 2007) show
strong evidence that plants of all types inhabiting a wide range
of ecosystems can transpire at night. This evidence suggests
that the notion that stomata always close in the dark is wrong.
The common occurrence of En and gn appears, thus, to be much
more widespread than has generally been acknowledged, and
in some instances, appears to be highly predictable (Figure 7).
NIGHTTIME TRANSPIRATION IN WOODY PLANTS
cause of the observed sap flux are required before the data can
be used quantitatively. We have more confidence in data obtained with the HRM because it excludes effects of thermal
gradients, it is accurate at low flow rates, and it can be used in
conjunction with xylem cutting to obtain an accurate zero reference.
An important question that is not fully resolved by any sap
flow method currently available is how to differentiate between nighttime flows partitioned into xylem refilling (from
depleted water stores) and En. We have suggested an approach,
as have Daley and Phillips (2006) and Fisher et al. (2007), to
differentiate refilling from En. Coupled with additional measurements such as gn, deuterium tracer data (Figure 8, Table 3), the measurement of volumetric changes unrelated to
growth using automatic high precision dendrometer bands
(e.g., Irvine and Grace 1997, Peramaki et al. 2001), as well as
placing HRM sap-flow sensors throughout the plant crown
(see Burgess and Dawson 2004), can help to better resolve this
important issue, while providing a robust way of quantifying
En and other important parameters such as stem capacitance.
For our examples, if all nighttime sap flow were simply due
to storage tissue refilling, it is unlikely there would be a strong
relationship between sap flow and nighttime VPD (Figures 1–5). One difficulty of interpretation is that there is typically a decline in VPD as the night progresses and air temperatures fall, which could match the decay function in sap flow
data that would indicate refilling. In this case, refilling and En
would be difficult to partition. Hinckley and Ritchie (1973)
overcame this problem with small trees by using plastic bags
that contained the plant and a wet towel. For larger trees, one
approach is to search for data where VPD drops rapidly at
dusk, so that refilling can be examined in the absence of a
driver for En. In such cases, where no decay in sap flow is detected, it can be inferred that refilling is small relative to En.
For example, in Figure 9, Night 12 shows a slight decay function that may partly be the result of a slight decrease in VPD,
but also appears to include refilling. Night 14, on the other
hand, has a decay function that matches that of VPD and we
can surmise from night 14 that very little of the sap flow was
due to refilling. Because the HRM can detect the low flow
rates found at night, we believe that it may be one of the best
ways to quantify and partition En and refilling. A second example of this approach is shown by Fisher et al. (2007) where
nighttime HRM traces often displayed two distinct phases; a
post-daylight decay phase and a constant phase that comes
some time later; both of these phases show sap flow rates
above zero and both occur at night. Fisher and colleagues suggest that the early sloped phase represents mostly xylem refilling and the later, non-zero linear phase represents nighttime
transpiration (see also Figure 6 in Fisher et al. 2007). This approach or the method advocated by Phillips et al. (1997) and
Daley and Phillips (2006) are useful for partitioning En from
refilling. Our approach is empirical, whereas Phillips et al.
(1997) predict transpiration rates with the JarvisMcNaughton model and compare the predicted En rates versus
rates obtained from sap flow measurements.
Ecophysiological implications
Understanding why En or gn occur is challenging given the
presently available data because most studies, including many
of our own, were not originally designed to investigate En or gn,
Figure 9. Heat pulse velocity (cm h – 1 ) as an indicator of nighttime
transpiration (En) in Eucalyptus salmonophloea and its relationship to
vapor pressure deficit (VPD, kPa) over five summer nights in 2004 at
Corrigin, Western Australia. Gray bands represent night. The thick,
black line is the sapflow trace and is closely associated with the daily
course of solar radiation. The light gray line is VPD, which peaks in
the afternoon when air temperature reaches its maximum and relative
humidity is usually at its lowest. Transpiration (sap flow) in this species of eucalypt peaks when solar radiation is maximal and leaf energy loads are highest.
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Figure 8. Percent change in the stable isotope composition of water
extracted from leaves and stems every 3 h for 15 h and then again after
30 h following deuterium labeling directly to the stem base (A) or to
the soil around the tree (B) (see Methods for details). Based on these
isotope enrichments, the transpiration rate was calculated (see Table 3). Gray bands represent night.
571
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DAWSON ET AL.
RU N − kHR ∆ΨU -R − En =
(1)
dΨ L
dΨS
dΨR
CR
+ CS
+ CL
dt
dt
dt
where RUN is nighttime root water uptake, CR, CS and CL are
root, stem and leaf specific capacitances, i.e., the change in tis-
sue water content (∆W) per unit change in water potential
(dΨ; Williams et al. 2001), kHR is hydraulic conductance associated with HR and ∆ΨU-R is the water potential gradient between the uptake and release layers of the soil profile (Lee et
al. 2005). Greater En will divert water that would otherwise be
available for both HR (kHR ∆ΨU–R ) or the refilling of internal
water stores (right-hand side of Equation 1). It is also apparent
from Equation 1 that if pressure–volume characteristics are
known, particularly the bulk elastic modulus of roots, stems
and leaves, then measures of water potential and sap flow
could be used to partition the proportion of nighttime sap flow
that contributes to refilling internal water reservoirs versus En.
Furthermore, for investigations of hydraulic lift or HR, it is
prudent to determine if En exists, because if it does, it could reduce the efficacy of these processes. Williams et al. (1993)
demonstrated that hydraulic lift increases when evaporative
demand is reduced by cloud cover; the corollary is also true,
and nighttime transpiration turns the canopy into a water sink
that competes with roots in dry soil.
The model presented above suggests that En may complicate
investigations that attempt to characterize cost–benefit relationships for comparative analyses (Westoby et al. 2002). Alternatively, if En is considered a plant trait with adaptive value,
e.g., by enhancing nutrient status at the expense of water status, then the occurence of En may produce tradeoffs that maximize partitioning of resources in plant communities with implications for species coexistence. Therefore, En should be
most beneficial in low-nutrient systems when soil water availability and nighttime VPD are high; for example, several days
of dry weather during the wet season in Mediterranean ecosystems could produce such conditions. If En were shown to be
more prevalent under such conditions, this would provide preliminary evidence that En is an adaptive process for plants.
Theoretical implications
The finding that En not only occurs but is widespread in plants,
and may represent a significant fraction of a plant’s daily and
seasonal water use, has several important implications for
plant water relations theory as well as for studies that utilize
plant water use data at larger scales. For example, if En occurs,
we need to modify our assumptions about the soil– plant–atmospheric continuum and, in particular, the assumption that
the drivers of water flux are important only during daylight
hours. This is relevant in parameterizing climate models,
where stable isotope data are used to partition plant and ecosystem carbon fluxes (see Seibt et al. 2007), as well as for accurate representation of site water balance. In cases where En
is documented, one might use the leaf-to-air vapor pressure
gradient, VPG, rather than solar radiation, as the primary
driver of transpiration. This then requires estimates of nighttime leaf temperatures, relative humidity and gn to calculate
the contribution of nighttime water loss. However, if gn varies
consistently with daylight g as a function of days after rainfall,
as shown in Figure 7, it may be possible to assess total plant
water loss (day and night) from measurement of daylight g
only. The relationship between g n /g and days after rainfall,
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nor were the methods standardized. Therefore, a meta-analysis
of En or gn is not easily accomplished, precluding quick identification of the possible reasons underlying the occurrence of
En and gn. We offer some hypothetical reasons that, if correct,
have important implications.
We are unaware of any direct evidence for why plants lose
water at night, yet some testable hypotheses for the general occurrence of nighttime transpiration, in longer-lived woody
plants in particular, can be stated. First, En may promote carbon fixation early in the daylight hours because it means that
stomata are already open, and photosynthetis can begin as
soon as light availability and temperature permit (see Oren et
al. 1999). This corresponds with what is observed in plants
from low-light environments which depend, for photosynthesis, on sunflecks (see Pearcy 1988). Second, and as suggested
by Scholtz et al. (2007), En could enhance nutrient supply to
distal parts of a woody plant crown. Third, continuous water
flux at night may serve to deliver O2 to parenchyma cells in
woody tissues where it is required for respiratory processes
(see Daley and Phillips 2006). This may be particularly important in large trees in which the availability of oxygen to tissues
is necessarily low because of the long diffusion path through
water-filled woody tissues. Finally, En may occur simply because stomata are prevented from closing for various possible
reasons, including by waxy plugs, leaf endophytes or asymmetrical guard cell complexes. It must also be the case that
some small fraction of En reflects cuticular water loss from
leaves, which likely increases as leaves age. To quantify the
importance of this pathway, however, better field methods are
required.
Under conditions where plants experience water deficit, En
may come at a cost by preventing plants from repairing embolized xylem conduits as would otherwise occur at night. In
addition, the lack of refilling of water storage tissues should
reduce overall transpiration the following day, because plant
storage reservoirs were not replenished overnight. Reduced
tissue water storage due to En would lead to lower tissue water
potential and greater risk of xylem cavitation and embolism
during times of high evaporative demand (Sperry 2000;
Buckley 2005). Many nights of En in succession may lead to a
repeated cycle that prevents plants from refilling their capacitors. This would lead to further cavitation and a reduced
chance of repair, thus impairing the important hydraulic resupply cycle that plants otherwise experience with daily stomatal closure.
By using a whole-plant water balance framework, we can
begin to see how En could reduce the efficacy of hydraulic redistribution (HR) as well as tissue capacitance, C, as:
NIGHTTIME TRANSPIRATION IN WOODY PLANTS
shown in Figure 7, may differ among species and for plants
growing under different soil water conditions, because days
following rainfall serves here only as a surrogate for plant water status. Thus, we expect that plant water status should provide a better and more general predictor of g n /g across species
and site conditions.
In the context of whole-plant water balance, we can see why
gn (or En) might depend on plant water status by rearranging
Equation 1 to give En as the residual of nighttime root water
uptake, the sum of the water losses through hydraulic redistribution and the change in water content of the main plant
capacitors:
En = RU N −
dΨ L
dΨ S
dΨ R
+ CS
+ CL
kHR ∆ΨU − R + C R
dt
dt
dt
(2)
site water budgets. High VPD, abundant soil water and species
with relatively insensitive stomatal function produce the conditions under which En is likely most important; most plants
experience one or more of these conditions at some point in
each and every growing season. The widespread occurrence of
En therefore requires us to: (1) rethink how to assess plant water relations; (2) choose appropriate sap flow measurement
methods; and (3) retool our transpiration models to include parameters such as nighttime leaf temperature, or gn, or both.
Acknowledgments
We thank Roman Pausch, Vanessa Boukili, Jia Hu, Eric Dubinsky,
Primrose Boynton and Kenneth Peer for their laboratory and field assistance. We are grateful for financial support provided by the US National Science Foundation (grants IBN-0308862 and DEB-0317139
to TD, DBI-0310103 to LS), the Cooperative Research Centre for
Plant-based Management of Dryland Salinity and the Australian Research council for research support to SB (Grant DP0344310), the
A.W. Mellon Foundation, Global Forest (Grants 18-2000-112 and
18-2000-113), The Save-The-Redwoods League, Cornell University
and U.C. Berkeley. Comments from Nathan Phillips, Nate McDowell
and Tom Hinckley on an early version of this manuscript were especially helpful in making our revisions. We also thank Tom for pointing
us towards some earlier literature on nighttime transpiration we had
overlooked. We thank Nathan Phillips and Margaret Barbour for organizing the special ESA session on this topic and inviting us to
participate.
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