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08 Associated changes in physiological parameters and spectral reflectance
indices in olive (Olea europaea L.) leaves in response to different levelsof water stress
P. SUN{, A. GRIGNETTI{, S. LIU{, R. CASACCHIA{, R. SALVATORI{,
F. PIETRINI§, F. LORETO§ and M. CENTRITTO*{{Institute of Forest Ecology, Environment and Protection, Chinese Academy of
Forestry, Beijing 100091, China
{CNR - Istituto sull’Inquinamento Atmosferico, via Salaria km 29.300, 00016
Monterotondo Scalo (RM), Italy
§CNR - Istituto di Biologia Agroambientale e Forestale, via Salaria km 29.300, 00016
Monterotondo Stazione (RM), Italy
(Received 1 December 2006; in final form 27 March 2007 )
This study aimed to determine whether modification of physiological parameters
could be detected remotely by monitoring the spectral reflectance of olive leaves
in response to different degrees of drought. Three different drought intensities
were simulated: (a) a mild drought by feeding abscisic acid to detached branches;
(b) a rapid and severe drought by detaching leaves and letting them dry over
several hours; (c) a relatively slow drought caused by withholding water to potted
olive plants. The three degrees of stress affected gas exchange and chlorophyll
fluorescence. When the inhibition of photosynthesis occurred within an hour it
was not accompanied by a parallel reduction in chlorophyll concentration in the
carotenoid to chlorophyll ratio. Consequently, changes in spectral reflectance in
the visible region, e.g. in PRI (photochemical reflectance index) and FRI
(fluorescence reflectance indices) were not significantly induced. In contrast,
when the inhibition of photosynthesis caused by slow developing drought was
prolonged (i.e. more than 24 hours) and led to a decrease in chlorophyll
concentration and to a simultaneous increase in carotenoid to chlorophyll ratio,
there were significant changes in the visible region of the leaf spectral reflectance
and, in turn, in PRI and FRI. We defined 16 new reference wavelengths, from
visible to SWIR regions, which are sensitive to both fast-developing and slow-
developing stresses. These reference wavelengths were used to develop an
algorithm, the Relative Reflectance Increment (RRI), that was linearly related to
changes in relative water content (RWC, r250.733). This algorithm showed that
the 1455 nm wavelength is highly affected by drought. This wavelength was
therefore used to elaborate the water content reflectance index that was inversely
related to RWC (r250.702).
1. Introduction
An important potential application of non-invasive remote-sensing techniques is to
monitor plant stress and photosynthetic status (Zarco-Tejada et al. 2003, Filella
et al. 2004, Dobrowski et al. 2005, Tian et al. 2005) and to provide information on
*Corresponding author. Email: [email protected]
International Journal of Remote Sensing
Vol. 29, No. 6, 20 March 2008, 1725–1743
International Journal of Remote SensingISSN 0143-1161 print/ISSN 1366-5901 online # 2008 Taylor & Francis
http://www.tandf.co.uk/journalsDOI: 10.1080/01431160701373754
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the occurrence and intensity of water stress (Ustin et al. 1998, Li et al. 2001, Goward
et al. 2002). Remotely sensed vegetation indices, particularly those associated with
water and nutritional status and, consequently, with various physiological and
ecological phenomena, are increasingly required for the assessment of terrestrial
ecosystem momentum transfer (Sellers 1997, Szilagyi 2000) and carbon uptake
(Veroustraete et al. 2002).
A large number of spectral indices have been developed to estimate plant water
status and physiological conditions by using different approaches. This is because
drought is a complex syndrome affecting several leaf biophysical and biochemical
properties. Water is an important leaf component, accounting for 50–80% of the leaf
fresh weight. Water absorbs radiation from the near infrared region to the
shortwave infrared region, with centres at approximately 970, 1200, 1450, 1950 and
2250 nm (Carlson et al. 1971, Gausmann et al. 1971, Hunt et al. 1987, Rollin and
Milton 1998). Consequently, a change in leaf water content can result in fairly broad
spectral change in these regions (Hunt and Rock 1989, Yu et al. 2000, Ceccato et al.
2001, Imanishi et al. 2004).
The earlier literature describes many studies focused on the development of
spectral indices for the detection of water stress (Carlson et al. 1971, Gausman et al.
1971, Hunt et al. 1987, Pierce et al. 1990, Carter 1991, Cibula et al. 1992, Penuelas
et al. 1993, Carter 1993). Bowman (1989) showed that in cotton the reflectance in the
near-infrared region increased as relative water content decreased. Aoki et al. (1988)
reported a close relationship between the leaf water content (LWC) per unit leaf area
and the reflectance ratio R1650/R1430 for woody plants. Imanishi et al. (2004) used
the shift of red-edge position of vegetation reflectance spectra for detecting LWC in
Quercus glauca and Q. serrata. Yu et al. (2000), working on herbaceous and woody
plants (i.e. Glycine max, Zea mays, Liriodendron tulipifera, and Viburnum awabuki),
estimated the relationships between reflectance and many leaf water status
parameters during leaf dehydration experiments, i.e. relative water content
(RWC), LWC, specific leaf water content, leaf moisture percentage on fresh weight,
and relative leaf moisture percentage on fresh weight basis. Other studies developed
spectral indices for detecting water content as percentage of dry mass (Gao and
Goetz 1995, Ustin et al. 1998) or in terms of equivalent water thickness at leaf level
(Ceccato et al. 2001). However, although all these parameters describing plant water
status may be useful for many different purposes, only RWC has a real physiological
meaning, because it measures the amount of water available for transpiration in
leaves and, as such, it is universally used to assess plant water relations (Tyree and
Jarvis 1982, Kramer and Boyer 1995). Moreover, there have been surprisingly few
studies that have examined the relationships between these components of plant
water status and spectral reflectance indices in response to different intensities of
water stress.
By causing changes in leaf physiological parameters and pigments concentration,
water stress affects reflectance spectral properties related to these processes
(Penuelas and Inoue 1999, Sims and Gamon 2002, 2003, Dobrowski et al. 2005).
A number of sensitive spectral indices were found in the visible region to estimate
foliar pigment concentration (Yoder and Pettigrew-Crosby 1995, Penuelas and
Filella 1998, Blackburn 1999, Jago et al. 1999, Sims and Gamon 2003, Tian et al.
2005). The photochemical reflectance index (PRI, R5312R570/R531 + R570) is a useful
index for estimating xanthophyll cycle pigments (Gamon et al. 1992, Penuelas et al.
1994, Gamon et al. 1997) and carotenoid/chlorophyll ratios (Sims and Gamon 2002)
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and, thus, plant photosynthetic status, but its efficacy is still unclear for detecting
physiological changes in response to different intensities of water stress. Recently, an
increasing interest is devoted to steady-state chlorophyll fluorescence for real-time
monitoring of plant photosynthesis and water status (Zarco-Tejada et al. 2000a,
2000b, 2003, Dobrowski et al. 2005). Their findings opened up new possibilities in
monitoring vegetation physiological changes using passive remote sensing strategies.
However, because of the fact that the contribution of the fluorescence signal, namely
the steady-state fluorescence (Fs) to spectral reflectance is very low (Dobrowski
et al. 2005), the reliability of using these spectral indices to detect photosynthetic
status in response to different intensities of water stress is also unknown.
When using remote sensing, improved knowledge about the relationship between
leaf reflectance indices and different intensities of drought appears to be important.
In this paper we present and discuss the results obtained in experiments focused on
determining which particular wavelengths and spectral indices may be most effective
in detecting physiological changes induced by differences in drought occurrences. In
particular we address two main issues: (1) how spectral reflectance is modified when
plants suffer from different degrees of drought, and (2) whether it is possible to
remotely detect by sensitive spectral indices different physiological changes induced
by different stress. For this purpose, three kinds of water stress were imposed: (1) a
mild drought was simulated by feeding abscisic acid (ABA) to detached branches
(Davies and Zhang 1991); (2) the occurrence of rapid, severe drought was simulated
by detaching leaves and leaving them to dehydrate on the bench; (3) a relatively slow
drought occurrence was caused by withholding water to potted plants. We
hypothesized that: (1) ABA feeding would only affect CO2 diffusional limitations
to photosynthesis, without affecting leaf water status and concentrations of nitrogen
and pigments; (2) leaf fast dehydration would affect both diffusional limitations to
photosynthesis and leaf water status, without affecting concentrations of nitrogen
and pigments; and (3) the slow drying cycle would affect all these parameters.
2. Materials and methods
Two-year-old plants of olive (Olea europaea L.) were grown in the greenhouse of the
Institute of AgroEnvironmental and Forest Biology, National Research Council,
Monterotondo (RM), Italy. Plants were grown in 15 dm3 pots containing a sand–
perlite mixture (1:3). To avoid any water and nutrient limitation, the saplings were
watered every other day to pot water capacity and fertilised once a week, with
complete nutrient solution at low concentration not to restrict needs of the trees.
2.1 Experiments
Three experiments were conducted in summer to simulate different intensities of
water stress:
(1) ABA feeding — Mild water stress was simulated by feeding abscisic acid (ABA)
to branches detached from well-watered plants of olive. Branches were cut
under distilled water and cis–trans ABA (99% purity, Sigma) was then added to
the water supplied to the branches to bring its concentration to 1024 M. Control
branches were kept in distilled water throughout the experiment.
(2) Fast leaf dehydration — The occurrence of rapid, severe drought was simulated
on detached leaves from the top and bottom leaves of the plants. Fully
expanded leaves were detached from well-watered plants of olive and left on the
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lab bench for three hours at 25uC. The leaves were weighed every hour to
determine the rate of water loss.
(3) Slow-developing water stress cycle — The olive saplings were kept at pot water
capacity until the beginning of June. Then half of the saplings (six plants) were
water-stressed by withholding water for a two-week drying cycle, simulating a
progressive decrease of water availability, while the other half of the saplings
were watered periodically to maintain the field capacity.
2.2 Gas exchange and fluorescence measurements
Leaf photosynthetic rates were measured by using a LI-6400-40 portable infrared
gas-analyser (Li-Cor, Lincoln, NE), allowing simultaneous measurement of gas
exchange and fluorescence. All gas exchange measurements were made between
10.00 and 15.00 h on the central section of a fully-developed leaf in ambient CO2
concentration. To enable measurements of photosynthetic rates at saturating
photosynthetically photon flux density (PPFD), leaves were illuminated using a red–
blue light source attached to the gas-exchange system and maintained at
1000 mmol m22s21. Leaf temperature was set at 25uC, and the relative humidity in
the leaf cuvette ranged between 47 and 50%. The fluorescence yield (i.e. the quantum
yield of PSII in the light, DF/F9m) was measured by using a saturating pulse
(10 000 mmol m22 s21) of white light (Genty et al. 1989).
2.3 Determination of relative water content, nitrogen and pigment concentrations
Leaf samples for relative water content (RWC), nitrogen and pigment concentra-
tions were taken immediately after the gas exchange measurements and spectral
measurements. Fully-developed leaves were recut under water and weighed to
determine leaf fresh mass (FM). After measuring leaf area, using a leaf area meter (LI
3100, LI-COR Inc., Lincoln, NE, USA), leaves were covered with a plastic bag and
allowed to rehydrate with the cut-end under water in a dark cold room at 5uC for
18 h. Immediately after rehydration, each leaf was weighed to determine the
saturated mass (SM), and then each leaf was oven-dried at 80uC for 48 hours to
determine dry mass (DM). Then specific leaf area (SLA) was calculated as dry mass
divided by the leaf area, whereas RWC was calculated as follows:
RWC~ FM{DMð Þ= SM{DMð Þ
The concentration of carotenoid and chlorophylls (Chl) a and b were measured in
intact leaf tissues by immersion in N,N-dimethylformamide (DMF). Leaf discs with
a total area of 1.5 cm22 were put in glass vials containing 2 cm3 DMF and
immediately placed in darkness at 4uC in an orbital shaker set to 100 rpm for 4 h
before absorbance (A) of the solution was read on a spectrophotometer (Perkin
Elmer, Norwalk, CT) at 663.8, 646.8, and 480 nm, using DMF as a blank. The
pigment concentrations were calculated according to the following equations
(Wellburn 1994):
Total chlorophyll azbð Þ~ 12|A663:8ð Þ{ 3:11|A646:8ð Þð Þ
z 20:78|A646:8ð Þ{ 4:88|A663:8ð Þð Þ
Carotenoid~ 1000|A480ð Þ{ 1:12|Chlað Þ{ 34:07|Chlbð Þð Þ=245
Nitrogen (N) concentration was measured following the wet digestion procedure for
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plant material (Allen 1989), on samples of freeze-dried, ground tissue, ranging in
mass between 95 and 105 mg. Nitrogen was measured colorimetrically with a flow-
injection analyser (FLOW 3000, Perstorp, Oregon, USA).
2.4 Spectral measurement and process
Spectral measurements were carried out in laboratory, by a portable spectroradiometer
(Field spec FR 350–2500 nm, ASD inc., USA), operating in the 350–2500 nm spectral
range. Fieldspec can acquire both radiance and reflectance data. The instrument
automatically calculates the reflectance value as the ratio between the incident
radiation, reflected from the surface target, and the incident radiation reflected by a
reference Spectralon panel. This material can be regarded as a Lambertian reflector.
Fieldspec may be operated with different lenses that control the field of view: in this
study an 8u lens was used to restrict the instrument field of view. Measurements were
taken in a dark room; the light source was an incandescent lamp. Reflectance spectra
were collected from a distance of 5 cm from the sample. Each spectral signature was
recorded as the average of 100 scans to reduce instrumental noise; a further check of
the stability of the reflected signal was performed by measuring the reflectance of the
reference panel at the beginning and end of each session. Reflectance spectra were pre-
processed by using the ViewSpecPro (ASD, Inc.) software.
Reference wavelengths were determined directly from the averaged reflectance
spectra of well-watered plants, while the inflection points were calculated by using
the first derivative reflectance spectra. Further spectral analysis and spectral indices
calculation of different drought treatments were performed on the basis of the
reference wavelengths. First derivative reflectance spectra were calculated as (Zarco-
Tejada et al. 2003):
LRi~ Riz1{Ri{1ð Þ= liz1{li{1ð Þ
where R is the reflectance and l is the wavelength.
The red edge (715 nm) was determined by identifying the peak wavelength in the
corresponding first derivative spectra between 680 nm and 750 nm.
Fluorescence ratio indices (FRI) were calculated as FRIR690/R600 and FRIR740/R800
(Dobrowski et al. 2005), whereas the photochemical reflectance index (PRI) was
calculated as (R5312R570)/(R531 + R570) (Gamon et al. 1990, 1997). The structural
independent pigment index (SIPI, i.e. a measure of carotenoids to chlorophyll a
ratio) was calculated as (R8002R445)/(R8002R680), and the normalized phaeophy-
tinization index (NPQI, i.e. a measure of chlorophyll degradation) was calculated as
(R4152R435)/(R415 + R435) (Penuelas and Filella 1998). The water index (WI) was
calculated as R900/R970 (Penuelas and Filella 1998). Moreover, the relative depth
index (RDI) (Rollin and Milton 1998) was used to describe leaf water absorption at
about 1140 nm in relation to the maximum reference wavelength at 1098 nm (Rmax)
and minimum reference wavelength at 1202 nm (Rmin):
RDI~ Rmax{Rminð Þ=Rmaxð Þ|100
To quantify and compare the change of reflectance spectra at different reference
wavelengths in response to water stress, we calculated relative reflectance increment
(RRI):
RRIli~ Rli{Rlcð Þ=RlC
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where l is the reference wavelength, i is the number of hours after the stress onset,
and c is control. RRI was also used to identify the most sensitive wavelength over
the course of water stress. Water content reflectance index (WCRI) was developed
to describe leaf water absorption feature between NIR and SWIR regions.
WCRI~RlSWIR= RlNIR{RlSWIRð Þ
lSWIR is the reference wavelength where the reflectance minimum at 1455 nm, i.e. the
reflectance at which the maximum RRI was observed in SWIR region, and lNIR is
the wavelength at 1272 nm, i.e. the reference wavelength where a reflectance peak
occurs in the NIR region.
2.5 Statistics
Data were tested using a simple factorial ANOVA (two-way maximum interactions)
and Post-hoc Tukey’s test. The statistical analysis was performed by SigmaPlot
(Systat software, Inc., 2004).
3. Results
The reference wavelengths identified were: 524 nm, 555 nm, 572 nm, 673 nm in the
visible region; 715 nm, 919 nm, 958 nm and 1098 nm in the near infrared region
(NIR); 1140 nm, 1202 nm, 1225 nm, 1272 nm, 1391 nm, 1455 nm, 1502 nm, and
1656 nm in the shortwave infrared region (SWIR).
3.1 ABA feeding
ABA feeding did not induce any change in chlorophyll and N concentrations (data
not shown). RWC was not significantly increased (data not shown); however,
stomatal conductance and photosynthesis (figure 1a) and fluorescence yield (i.e. the
quantum yield of PSII in the light, DF/F9m) (figure 1b) decreased rapidly. A small
modification in the NIR of the spectral reflectance (figure 2a), which partly reflects
cellular scattering by leaf water content, was observed. This may reflect the slight
increase in RWC, whereas the changes in the photosynthetic properties were not
reflected by parallel modification in leaf spectral reflectance in the visible region
(figure 2a). The FRIR690/R600 and FRIR740/R800 and photochemical reflectance index
(PRI) showed no significant change during the ABA treatment (figure 3).
3.2 Fast leaf dehydration
In both top and bottom leaves, RWC decreased most rapidly during the first hour,
and then the water loss proceeded at slower rate (figure 4). Leaf dehydration
decreased leaf gas exchange properties significantly (data not shown), but did not
cause any changes in chlorophyll and N concentrations (data not shown). The
reduction of gas-exchange and fluorescence were not mirrored by changes in spectral
reflectance in the visible region (i.e. at wavelengths of 400–700 nm) (figure 2b).
Consequently, FRI and PRI were not affected by leaf dehydration (data not shown).
However, spectral changes in NIR and SWIR regions were consistent with changes
in RWC. RRI showed large changes especially at 715 and 1098 nm (NIR region) and
at 1391, 1455, 1502, and 1656 nm (SWIR region) (figure 5a). The changes of RRI in
the SWIR region, particularly at 1455 nm, were the most sensitive to leaf
dehydration (figure 5a). RRI increased markedly after the first hour of leaf
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dehydration (i.e. when water loss was particularly high, also causing a RWC
decrease of ,10%), reaching the value of ,0.3 at 1455 nm. Afterwards, RWC
decreased at a lower rate and this was mirrored by a lower rate of RRI increase. The
reflectance index reached a value of ,0.45 at 1455 nm after four hours of leaf
dehydration (figure 5a). RRI at 1455 nm was linearly correlated to RWC (r250.733)(figure 5b).
3.3 Slow-developing water stress cycle
As no significant differences in the physiological parameters and the reflectanceindices measured on top and bottom leaves were found, the data were pooled. Water
stress induced large changes of photosynthesis, stomatal conductance and
fluorescence yield (table 1). These parameters were dramatically reduced after five
days of water stress (i.e. when the stress was moderate and RWC was slightly
affected), and further decreased at the end of the experiment, when RWC was
reduced by an average of 28% (table 1). The moderate water stress (after a five-
daytreatment) did not induce any change in total chlorophyll concentration,
whereas at the end of the experiment chlorophyll concentration was significantlyreduced by an average of 16% in top leaves and 23% in bottom leaves. Leaf
carotenoid to chlorophyll ratio increased significantly after 15 days. On the other
Figure 1. Time course of (a) photosynthesis (A) and stomatal conductance (gs) and (b)chlorophyll fluorescence (DF/F9m) in response to ABA feeding to branches detached fromwell-watered olive saplings. The measurement conducted immediately after the branches werecut and dipped into the pure water (time 0), and at one, two, three and four hours after ABAfeeding, respectively. Data are means of eight plants ¡1 SEM.
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hand, N concentration and SLA were not significantly affected by water stress cycle
in either leaf types (table 1).
The slow-developing water stress treatment dramatically affected the spectral
reflectance of olive leaves (figure 2c). As for the photosynthetic parameters, also PRI
(the photochemical reflectance index) and the R690/R600 ratio decreased gradually
from the onset of water stress to the end of the water stress cycle (table 1). However,
the R740/R800 ratio was not affected by water stress and, consequently, was not
correlated to changes of physiological properties. As water stress increased in
Figure 2. Modification of the reflectance spectra in (a) ABA treated leaves, (b) detachedleaves from well-watered olive saplings and (c) in leaves of olive saplings in well-wateredplants (control) and water-stressed plants after five and 15 days from the onset of water stress.In ABA treated and detached leaves, each reflectance spectra is a mean of 20 samples, whereasduring the water stress cycle each reflectance spectra is a mean of 48 samples (including bothtop and bottom leaves).
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Figure 3. Time course of (a) fluorescence reflectance indices and (b) photochemicalreflectance index (PRI) in response to ABA feeding to branches detached from well-wateredolive saplings. R690/R600, R740/R800 are reflectance indices calculated by using bands located atthe chlorophyll emission maxima normalized by bands not affected by chlorophyllfluorescence emission (600 nm and 800 nm) (Dobrowski 2005). Data are means of eightplants ¡1 SEM, three replicates of reflectance spectra were measured per leaf.
Figure 4. Time course of relative water content (RWC) during dehydration of leavesdetached from well-watered olive saplings. Data are means of 20 leaves ¡1 SEM.
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intensity, the red edge position was progressively shifted to shorter wavelengths and
NPQI was significantly decreased, whereas there was no effect on SIPI and WI
(table 1). The slow-developing water stress also significantly affected RRI,
particularly when it was measured at reference wavelengths in the visible region(figure 6). At the end of the drying cycle, RRI increased in all reference wavelengths,
showing, however, the strongest increase in both visible and SWIR regions. RRI
measured at 1455 nm was found again to be the most sensitive wavelength to water
stress. As seen in the leaf fast dehydration experiment (figure 5b), the increase of
RRI at 1455 nm might correlate with the strong decrease in RWC caused by severe
water stress (table 1). The reference wavelength at 1455 nm was also used to calculate
the water content reflectance index (WCRI). WCRI was inversely related to RWC
(r250.702) (figure 7a). However, the accuracy of this correlation was similar to thatfound in the linear relationship between the relative depth index (RDI) and RWC
(figure 7b).
Figure 5. Relative reflectance increment (RRI) changes at different reference wavelengthsover the course of leaf dehydration (a) and relationships between relative reflectanceincrement (RRI) at 1455 nm and relative water content (RWC) (b).
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4. Discussion
This study aimed to determine whether modification of physiological parameters
induced by water stress could be detected remotely by monitoring the electro-
magnetic energy (from visible to SWIR regions) reflected by olive leaves. There were
Table 1. Total chlorophyll (Chl, mg cm22) and nitrogen (N, g g21) concentration on leaf areabasis, leaf carotenoid to chlorophyll ratio (Carot/chl), relative water content (RWC), specificleaf area (SLA, cm2 g21), photosynthesis (A, mmol m22s21), stomatal conductance (gs,mol m22s21), fluorescence (DF/F9m), Water Index (WI), structural independent pigment index(SIPI), normalized phaeophytinization index (NPQI), relative depth index (RDI), red edgeposition, photochemical reflectance index (PRI), and fluorescence reflectance indices(FRIR690/R600 and FRIR740/R800) determined on leaves of olive saplings after five and 15days from the onset of water stress. Data, pooled from top and bottom leaves, are means of 48leaves (four per plant) ¡1 SEM. Letters (a, b, c) indicate significant differences at P,0.05 in
the same line.
Control 5-day stress 15-day stress
A 9.87¡0.98 a 1.21¡0.38 b 0.88¡0.29 cgs 0.240¡0.037 a 0.019¡0.003 b 0.015¡0.004 bDF/F9m 0.301¡0.023 a 0.176¡0.017 b 0.075¡0.016 cChl 40.9¡3.5 a 39.3¡4.9 a 34.2¡2.6 bN 1.20¡0.10 1.15¡0.20 1.15¡0.10Carot/Chl 0.215¡0.010 b 0.234¡0.015 b 0.292¡0.020 aRWC 0.93¡0.03 a 0.87¡0.02 b 0.68¡0.03 cSLA 39.6¡1.5 40.0¡1.6 38.9¡1.2WI 1.02¡0.01 1.01¡0.03 1.01¡0.02SIPI 0.969¡0.003 0.969¡0.002 0.972¡0.002NPQI 0.224¡0.017 a 0.155¡0.007 b 0.129¡0.010 cRDI 15.78¡0.42 a 16.06¡0.29 a 12.33¡0.59 bRed edge 716¡1 a 712¡1 b 707¡1 cPRI 26.9?1023¡0.3?1023 a 23.4?1022¡0.2?1022 b 27.7?1022¡0.4?1022 cFRIR690/R600 0.87¡0.03 a 0.80¡0.03 b 0.71¡0.03 cFRIR740/R800 0.88¡0.02 0.90¡0.04 0.89¡0.03
Figure 6. Relative reflectance increment (RRI) determined at different reference wave-lengths in water-stressed olive saplings after five and 15 days from the onset of water stress.Data are means of 48 leaves ¡1 SEM.
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no statistical differences in the physiological parameters and in the associated
reflectance spectrum in both top and bottom leaves, presumably because the plants
being young and with a limited canopy the bottom leaves had not yet developed as
shade leaves, and for this reason the data of the different leaf types were combined.
To establish reflectance indices and parameters that can be used for effectively
evaluating water stress, an algorithm (RRI) and 16 reference wavelengths were
developed (figures 5 and 6). Inhibition of gas exchange and fluorescence induced by
water stress which occurred over an hour timescale was not accompanied by parallel
reduction in chlorophyll concentration and an increase in the carotenoid to
chlorophyll ratio. Therefore, changes in spectral reflectance in the visible region
were not significantly induced (figures 2a and 2b), whereas simultaneous reductions
of the photosynthetic pigments and photosynthetic activity (table 1) induced by slow
water stress resulted in significant changes in the visible region of the leaf spectral
reflectance (figures 2c and 6). In an attempt to improve the remote detection of the
Figure 7. Relationships between relative water content (RWC) and (a) water contentreflectance index (WCRI) (r250.702) and (b) relative depth index (RDI) (r250.698) in well-watered plants (control) and water-stressed plants after five and 15 days from the onset ofwater stress.
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water status of the leaves a new water stress-related reflectance index (WCRI) was
developed (figure 7a).
A large number of spectral indices have been developed for estimating leaf
physiological status (e.g. Gamon et al. 1992, Gao and Goetz 1995, Ustin et al. 1998,
Yu et al. 2000, Zarco-Tejada et al. 2000a, Ceccato et al. 2001, Muttiah 2002,
Imanishi et al. 2004). RWC is universally used to detect the water status of plants
(Tyree and Jarvis 1982, Kramer and Boyer 1995), but until now correlations with
spectral indices have been made with other water status parameters (e.g. LWC per
unit leaf area, specific leaf water content, leaf moisture percentage on fresh weight,
relative leaf moisture percentage on fresh weight basis, etc.) which are not used in
studies on plant–water relations in the soil plant atmosphere continuum. Moreover,
because these indices have been tested only in a limited number of species, it is not
yet clear whether these indices are species-specific or whether their use can also be
extended to different plant functional types (Blackburn 1998, Sims and Gamon
2002, Bryant and Baird 2003). Furthermore, these indices may also show
intraspecific variations caused by different physiological conditions (Horler et al.
1983).
The term ‘reference wavelength’, as it has appeared in a number of previous
reports (Serrano et al. 2000, Sims and Gamon 2002, 2003), cannot be universally
applied for the effective evaluation of the water status of plants. Reference
wavelength was generally defined as a constant wavelength between 750 and 900 nm,
i.e. outside the chlorophyll absorption bands (Sims and Gamon 2002), and
consequently it has limited applications. For this reason, in this study, the
connotation of this term was extended by identifying a series of typical wavelengths
at the reflection peaks, valleys, and inflection points (maximum slope) of the control
leaf reflectance spectra from visible to SWIR regions. Thus, a new series of reference
wavelengths were defined and tested to see whether these wavelengths were suitable
indicators of different degrees of water stress. After identifying the reference
wavelengths, the corresponding reflectance values were determined in control
plants. These values were then used to compute the spectral reflectance changes in
water-stressed plants, allowing calculation of the Relative Reflectance Increment
(RRI) (figures 5 and 6). Differently from the spectral subtraction technique (Zarco-
Tejada et al. 2003), RRI shows the relative changes rather than absolute changes in
the spectral reflectance (Carter 1991). Consequently, even small changes in the
spectra can be effectively detected by RRI, for instance at low-reflective wavelengths
(i.e. visible region) where usually not large changes occur in response to water stress.
Thus, this new algorithm was used to identify the most sensitive wavelengths of the
spectral reflectance affected by water stress (figures 5a and 6) (Carter 1991).
Our study showed that the reflectance spectra in the visible region (figures 2a and
2b) and, consequently in PRI and FRI (figure 3), were not influenced when stomatal
closure and photosynthesis inhibition (figure 1) occurred within an hour and,
consequently, were not long enough to cause changes in the concentration of
photosynthetic pigments. This was the case of our experiments with ABA feeding
and fast leaf dehydration (data not shown). Similarly, Foley et al. (2006) also
showed that leaf reflectance in the visible region in five tropical trees was not
responsive to water content changes that occurred within an hour. This is often the
case in nature, when diurnal stresses develops in hot summer days, or in response to
vapour pressure deficit (Alvino et al. 1994, Centritto et al. 2000). It still remains
difficult to correctly assess these rapidly inducible and relieved physiological
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changes by remote indices. Recent studies suggested a strong relationship between
steady-state fluorescence (Fs) and photosynthesis under variable irradiance and
water stress conditions (Flexas et al. 2002, Dobrowski et al. 2005). These studies
may indicate the possibility to assess photosynthesis changes due to transient
stomatal closure by using FRI. However, both our ABA and fast leaf dehydration
experiments have demonstrated that FRI does not follow the decline of the
fluorescence parameter DF/F9m, which is also based on Fs measurements (Genty et
al. 1989). This is probably because ABA feeding (figure 3a) and fast leaf dehydration
(data not shown) did not induce significant changes in Fs, or small changes of Fs
signals have no effect on spectral reflectance index. The contribution of Fs to the
spectral reflectance is known to be very low (e.g. up to 2%, Zarco-Tejada et al.
2003), and this contribution may also be highly variable (Dobrowski et al. 2005).
Dobrowski et al. (2005) also attributed less than 1% of the canopy reflectance
change to Fs changes, in Vitis vinifera subjected to a diurnal heat and water stress.
Although Fs changes in response to transient water stress were detected in Acer
saccharum by using a time-decay experiment and induction with long-pass filters
(Zarco-Tejada et al. 2000a, 2000b), the estimation of photosynthetic status by FRI is
still a challenge.
On the other hand, when the rapid dehydration was associated with a decrease of
RWC, such as in the fast leaf dehydration experiment, this could be remotely
followed by measuring associated changes of the RRI in the NIR and SWIR areas
(figure 2b). Increased reflectance in reference wavelengths in both NIR and SWIR
regions of the leaf spectrum are known to indicate a decrease in leaf water content
(Carter 1991, Hunt and Rock 1989, Ceccato et al. 2001, Muttiah 2002). These
changes were indeed associated with the rapid dehydration of the leaf in a number of
different reference wavelengths (figure 5a). The most sensitive wavelengths to RWC
changes could be distinguished by RRI. The RRI measured at 1455 nm increased
faster than at other reference wavelengths, and was identified as the most sensitive
wavelength to RWC changes (figure 5b). This confirms earlier suggestions that the
wavelengths near 1450 nm are among the most sensitive bands to changes in water
content (Carter 1991, 1993). Reference wavelengths in the SWIR region (i.e.
1502 nm, 1391 nm and 1656 nm) were also found to be more sensitive than other
wavelengths in NIR region to RWC changes (figure 5a). This can be explained by
the strong water absorption capacity in the SWIR bands (Palmer and Williams
1974, Carter 1993).
The slow-developing water stress cycle experiment was perhaps the most
representative of natural conditions. This causes reductions of RWC associated
with changes in the structural components of the leaves, including pigments (table 1)
and other organic molecules (Bray 1997, Chaves and Oliveira 2004, Centritto 2005).
Whether a reflectance index was particularly suitable to monitor the occurrence of
physiological changes caused by this stress was investigated.
The photochemical reflectance index (PRI) was originally developed to estimate
rapid changes in the xanthophyll cycle that occur over a minute timescale and are
related to changes in photosynthetic light use efficiency (Gamon et al. 1992, 1997).
Differently from ABA feeding and rapid leaf dehydration, PRI showed a significant
decrease as water stress progressed (table 1). This may be related to the strong
inhibition in the photosynthetic activity due to prolonged drying over a day
timescale which led to a decrease in chlorophyll concentration and to a simultaneous
increase in the carotenoid to chlorophyll ratio (table 1 and Sims and Gamon 2002).
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The decrease in chlorophyll concentration was mirrored by the parallel decrease in
NPQI, which is according to Penuelas and Filella (1998) a measure of chlorophyll
degradation, whereas there was no correlation between the biochemical measure-
ments of the carotenoid to chlorophyll ratio and the indirect measurements of the
carotenoid to chlorophyll (i.e. SIPI). However, a decrease of photosynthetic light
use efficiency was also observed in response to the slowly developing water stress, as
inferred from the photosynthesis reduction at a PPFD of 1000 mmol m22s21 and by
the reduction of the fluorescence index DF/F9m at the same light intensity in turn
probably linked to an increased dissipation by xanthophyll deep-oxidation
(Demmig-Adams and Adams 2000, Demmig-Adams 2003). Thus, the influence of
these two components of PRI could not be separated.
The FRIR690/R600 also showed reductions as the water stress progressed and may
reflect a corresponding decrease in DF/F9m (table 1). This, in turn, may indicate a
significant decrease of Fs as found by Dobrowski et al. (2005). In contrast, the
FRIR740/R800 did not show any change throughout the course of water stress cycle
(table 1). Thus wavelengths in the NIR region may not only refer to water stress but
may also indicate structural changes over the 15-day water stress cycle, such as
ontogenetic variations of SLA (table 1) or dry mass (Muttiah 2002).
As also indicated by the fast-developing stress experiment, the 1455 nm
wavelength is highly sensitive to water stress (figures 5a and 2b). However, because
of the limited time series of data in the slow-developing water stress experiment, the
relationship between RRI (at 1455 nm) and RWC, as shown in figure 5b for the fast-
developing stress, could not be estimated. Therefore an index based on the 1455 nm
response, the WCRI, was developed for detecting RWC and, consequently, the
intensity of water stress. Simultaneously, the RDI index was applied to the
estimation of RWC. RDI was measured in the NIR region and was found to be
positively correlated in field conditions to the percentage of canopy water content in
a grassland (RDI centred upon 1150 nm and normalized with the 1116 nm band)
(Rollin and Milton 1998), and to the percentage of leaf water contents in wheat
subjected to different irrigation treatments (RDI centred upon 965–1085 nm spectral
regions and normalized with the 1192–1282 nm spectral regions) (Zhao et al. 2004).
A similar relationship with RWC was found when using both WCRI (figure 7a) and
RDI (figure 7b). However, this relationship was clear at low RWC values (after a 15-
day stress), while it was weak during the first phase of the stress (i.e. high RWC
values). Thus, both indices still need to be refined in detecting plant water status by
remote sensing. However, we speculate that because WCRI is centred on a band (i.e.
1455 nm wavelength) which is very sensitive to water stress, it could result in a more
useful index to estimate leaf water status in olive and similar sclerophyllous plants
by proximal sensing. However, because of the scattering due to atmospheric
pollution (Cartalis and Varotsos 1994, Kondratyev and Varotos 2001), also
absorption by the atmospheric water vapour is very strong at 1455 nm.
Consequently, WCRI may prove to be inadequate in assessing water stress from
airborne and satellite platforms.
It should be noted that the physiological significance of the reflectance indices is
dependent not only on physiological activities but also on the density of vegetation.
There are suggestions from previous studies that NIR wavelengths, e.g. water
indices namely R900/R970 (Penuelas et al. 1993) and the ratio between 1150 and
1260 nm (Sims and Gamon 2003), penetrate further into canopies and thus might
allow better estimation of water content in thick canopies. However, the surface
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layer of the canopy is also the photosynthetically active layer, and thus RWC (and
associated reflectance indices such as the WCRI) of surface canopies may still be an
important indicator of physiological drought in thick canopies.
To summarize, the following questions have been investigated: (1) how spectral
reflectance is modified when plants are subject to different degrees of drought, and (2)
whether it is possible to remotely detect by sensitive spectral indices physiological
changes induced by different degrees of stress. In this study, 16 new reference
wavelengths, a new water stress-related reflectance index (WCRI) and a new algorithm
(RRI) were developed to improve detection of water stress by spectral reflectance
changes. When the inhibition of gas exchange and chlorophyll fluorescence induced by
water stress was not accompanied by parallel reduction in pigment concentrations,
changes in spectral reflectance in the visible region were not significantly induced.
However, changes of leaf water status induced by both fast-developing and slow-
developing stress were detected, and reduction of both photosynthetic pigments and
photosynthetic activity induced by slow-developing water stress were also detected by
monitoring changes of the leaf spectral reflectance and this may have interesting
applications for both proximal and remote sensing of water stress.
Acknowledgements
This research was funded by the national Natural Science Foundation of China
(NSFC) (No. 30471383), national Key Fundamental Research Plan of China
(No. 2002CB111504), key joint research project of NSFC (No. 30590383), key
Laboratory of Forest Ecology and Environment of State Forestry Administration,
and by the Agreement of Scientific Cooperation between the Consiglio Nazionale
delle Ricerche of Italy and the Chinese Academy of Forestry of P.R. China. We
would like to thank Dr. Maria Soprano for the nitrogen analysis, Dr. Ulo Niinemets
and Prof. Josep Penuelas for helpful comments. We thank two anonymous reviewers
for their constructive and helpful comments on the manuscript.
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