Stomata play a key role in plant adaptation to changing environmental conditions as they control both water losses and CO2 uptake. Particularly, in the context of global change, simulations of the consequences of drought on crop plants are needed to design more efficient and water-saving cropping systems. However, most of the models of stomatal conductance (gs) developed at the leaf level link gs to environmental factors or net photosynthesis (Anet), but do not include satisfactorily the effects of drought, impairing our capacity to simulate plant functioning in conditions of limited water supply. The objective of this review was to draw an up-to-date picture of the gs models, from the empirical to the process-based ones, along with their mechanistic or deterministic bases. It focuses on models capable to account for multiple environmental influences with emphasis on drought conditions. We examine how models that have been proposed for well-watered conditions can be combined with those specifically designed to deal with drought conditions. Ideas for future improvements of gs models are discussed: the issue of co-regulation of gs and Anet; the roles of CO2, absissic acid and H2O2; and finally, how to better address the new challenges arising from the issue of global change.
Stomata consist in pores scattered over the relatively waterproof and CO2-tight cuticle covering the leaf surface. They play an essential role in controlling both water losses by transpiration and CO2 uptake for photosynthesis and plant growth. Stomatal aperture is controlled by the turgor pressure difference between the guard cells surrounding the pores and the bulk leaf epidermis. Changes in the turgor of the guard cells can be very quick, thus allowing for fast adaptation to rapidly changing conditions. This capacity to respond quickly is essential for plants which have to optimize CO2 uptake and water losses in continually fluctuating environmental conditions. Stomata also play a key role in modulating the transpiration-driven water flow through the soil–plant–atmosphere continuum, and consequently determine the rate of soil water depletion. Eventually, stomata play a very important role in preventing leaf surfaces from reaching excessive temperatures through the control of plant transpiration they provide and its associated cooling effect. Because stomatal regulation plays a key role in plant adaptation to changing environmental conditions and to stress, it appears of paramount importance to try to improve our understanding of the way stomata respond to environmental parameters and optimize their responses in the presence of often conflicting priorities.
Stomatal aperture is sensitive to multiple environmental influences. Among them, drought appears of particular concern to plant ecophysiologists. Water stress has indeed detrimental effects on community development of natural plants, and growth and productivity of crops. In the coming years and decades, as a consequence of global change, drought events are expected to strengthen in terms of intensity, frequency and geographic expanse (IPCC 2007). This issue will become all the more important that world water supply is limiting, while demand for food and water for irrigation will raise along with the human population (Somerville & Briscoe 2001). There is thus an increasing need to anticipate the consequences of drought on crop plants, with the objective to design more efficient and water-saving cropping systems.
Modelling appears as the most effective and well-adapted tool for integration, simulation and prediction purposes. Carbon assimilation, water losses and stomatal aperture – estimated by the stomatal conductance to CO2 and H2O, gs– are among the functions that have been the most extensively modelled during the last 40 years. Some approaches, particularly in ecology, have described the global response of vegetation (Reichstein et al. 2002). Global models are very useful, but they are generally incapable to provide an insight into the mechanisms through which stomata respond to environmental conditions. Among the numerous modelling approaches at the leaf level, many are essentially empirical, based on statistical correlations between environmental or internal factors and gs, and very few are really mechanistic. The majority of stomatal conductance models are ‘semi-empirical’ (i.e. built on physiological hypotheses, but still combined with empirical functions). Most of these models focus on one or two factors that affect stomatal aperture. For many years, gs models did not include the effects of drought, impairing our capacity to model plant functioning in conditions of limiting water supply. Following the increasing awareness of the importance of drought, more and more empirical or semi-empirical functions of water stress have been implemented into models previously constructed for non-stress conditions. These models are based on the different approaches reviewed below.
Responses of stomata to the local environment of the plant (soil water status, light, air humidity, temperature and atmospheric CO2 concentration) have been studied for decades and were the subject of an abundant literature. The pattern of each individual response has been extensively described (Jarvis 1976; Jones 1992; Monteith 1995). Underlying mechanisms have been partially elucidated, but there are still missing pieces and links to bridge the gap between environmental conditions, how they are sensed and transduced into whole plants and how they end in stomatal responses. This hampers the development of integrative approaches of stomatal responses to multiple environmental influences where possible couplings and interactions could be taken into account. Gathering the missing pieces and links appears of particular importance in the context of global change because combinations of environmental shifts are expected. How stomata will integrate changes in CO2 concentration, temperature, air and soil humidity directly questions the way the signalling cascades interact from the plant to the cell level. The rate of stomatal response to fluctuating environmental conditions should also deserve attention. Slow response of stomata to rapid changes in conditions like sunflecks introduces distortion from steady state and requires proper parameterization of gs models (Stegemann, Timm & Kuppers 1999). However, this last aspect will not be covered in this review considering, like the vast majority of models, that stomata follow a succession of steady states.
Plant responses to environmental stimuli are mediated from short to long distances by many internal signals such as hormones, reactive oxygen species (ROS), CO2 concentration in the leaf intercellular space and hydraulic signals (Hetherington & Woodward 2003). Within the leaf epidermis, solute accumulation and redistribution between the different cell types and compartments also play a major role in the regulation of cell turgor and the turgor-driven stomatal movements (Schroeder et al. 2001). In guard cells, numerous molecular actors are involved in solute transport, ranging from membrane ion channels and transporters to ATPases, regulating proteins, cytoplasmic Ca2+ or pH (see the reviews of Schroeder et al. 2001; Roelfsema & Hedrich 2005; Pandey, Zhang & Assman 2007). The way guard cells integrate signalling cascades remains still incompletely understood. In the absence of a true understanding of the underlying mechanisms, modelling approaches remain fragmental. There have well been a few attempts to propose integrated views of molecular cascades triggering stomatal response to drought. Such approaches are mainly based on the key role of abscisic acid (ABA) on ion trafficking and osmotic regulation in guard cells (Pei et al. 2000; Schroeder et al. 2001; Roelfsema & Hedrich 2005; Li, Assmann & Albert 2006). Although they provide a very stimulating view of the determism of stomatal movements, they remain purely qualitative because information remains fragmental.
Optimization theories can be effectively exploited to combine multiple individual responses to each environmental influence into simplest models. In most conditions, plants tend to maximize CO2 assimilation for a fixed amount of water loss, or tend to minimize water loss for a fixed amount of CO2 assimilation, which is equivalent (the so-called stomatal optimization theory) (Cowan 1977; Cowan & Farquhar 1977). Using Lagrange transformation, this translates mathematically into the assumption that stomata behave in such a manner that the ratio of the sensitivities of the rates of transpiration (E) and net carbon assimilation (Anet) to changes in gs (the marginal water cost per unit carbon gain ∂E/∂Anet) remains constant and equal to the Lagrange multiplier λ over a given time-frame. However, λ was shown to vary with environmental conditions, mainly with soil moisture (Cowan 1982; Makela, Berninger & Hari 1996; Thomas, Eamus & Bell 1999; Buckley 2008). The optimization theory thus states that ∂E/∂Anet does not vary taking water supply as an a priori constraint, captured by λ. On a daily time-scale, soil and air moisture can be considered as constant, and so can be λ. Under these conditions, it is mathematically demonstrated that E/Anet[or Anet/E, the photosynthetic water-use efficiency (WUE)] remains constant. It has also been hypothesized that stomatal aperture is controlled so as to maintain CO2 concentration in the intercellular space (Ci) almost constant whatever the changes in light (but under conditions of steady soil and air water status), which actually translates into a stable gs-to-Anet ratio or WUE (Wong, Cowan & Farquhar 1978; Norman 1982; Ball, Woodrow & Berry 1987; Mott 1988; Aphalo & Jarvis 1993). This assumption is consistent with the optimization theory developed above in that sense that stomatal response and photosynthetic acclimation tend to preserve the relative contributions of biochemical and diffusion limitations to CO2 uptake. The Ci conservative assumption has been supported by experimental results (e.g. Leuning 1995), and was incorporated into models of whole-plant transpiration where stomatal conductance is a function of assimilation rate (Tuzet, Perrier & Leuning 2003). Because the assimilation rate is in turn sensitive to light, CO2 partial pressure and temperature, such models are supposed to indirectly encapsulate the responses to these climatic factors. However, most models based on the Ci conservative hypothesis do not take into account the impact of soil water stress (Vico & Porporato 2008). In conditions of water deficit (captured by λ), the hydraulic theory states that stomatal closure occurs to prevent the formation of embolism in xylem vessels. The hydraulic theory implies that stomata are also regulated so as to maintain the xylem water potential above a critical cavitation threshold (Ψcav). The optimization theory of stomatal functioning and the hydraulic theory of stomata regulation were proven successful when applied for modelling purposes.
The objective of this review was to draw an up-to-date picture of the gs models that have been proposed so far, along with their mechanistic or deterministic bases. It mainly focuses on models capable to account for multiple environmental influences with special attention to drought conditions. We examine how models that have been developed for conditions characterized by the absence of water deficit can be combined with those specifically designed to deal with drought conditions. A critical review is provided of the various models that have been proposed so far, from the empirical ones designed for field studies, to the more complex, process-based ones. Table 1 summarizes the major characteristics of these models: major hypothesis, response to water stress, coupling with a photosynthesis model and number of parameters. We also provide an evaluation of ease-of-use. Finally, we discuss some ideas for future improvements of models of gs, among others to better address the new challenges arising from the issue of global change.
Table 1. Major characteristics of the models of gs
Water stress response
Number of parameters
For each model, the equation number (Eqn) reports to Table 2. In the column ‘number of parameters’, parameters that can be estimated independently are mentioned preceded by +.
Stomatal movements are governed by turgor pressure of guard cells and bulk leaf epidermis Mechanical advantage of epidermal cells
Theoretical use – parameterization at cell level
It is important to note that, because of the differences in diffusion coefficients existing between water vapour and CO2, stomatal conductance to H2O (gs,w) is 1.6 times higher than stomatal conductance to CO2 (gs,c). For the sake of clarity, this paper will only deal with gs,w, noted gs.
A list of all variables and parameters used in this review is provided in Table 2.
Table 2. Equations relative to the models of gs
Complex functions are not detailed and are written as f(main variables). Abbreviations not listed in Table 3 are empirical constants.
Osmotic potential gradient between epidermal and guard cells
Water potential gradient between epidermal and guard cells
Soil water deficit
Leaf-specific hydraulic resistance to water flow through the plant (roots–stomata)/constant
Guard cell osmotic potential
Water potential at point A (B)
Epidermal cell water potential
Guard cell water potential
Leaf water potential
Pre-dawn leaf water potential
Root water potential
Soil water potential
Water potential at which the xylem conductivity equal 0 (100% embolism)
CO2 compensation point
Volumetric soil water content at wilting point
Volumetric soil water content at field capacity
Volumetric soil water content
STOMATAL CONDUCTANCE MODELS IN THE ABSENCE OF WATER STRESS
Empirical models of responses to climate
Light intensity (Q) is certainly the most fluctuating factor that modulates stomatal aperture; gs is correlated with Q through a non-linear asymptotic relationship. In accordance with their role in water loss regulation, stomata also close with decreasing air humidity (Lange et al. 1971) or alternative-related variables such as water vapour pressure deficit (VPD) (Aphalo & Jarvis 1991; Monteith 1995). Concentration of CO2 in the ambient air (Ca) is also negatively correlated to stomatal aperture. Lastly, air temperature influences stomatal aperture. The response to temperature can be represented either by a more or less linear function or by an optimum response curve (Jarvis 1976; Jones 1992). We present in this section the most current empirical models based on the observed responses of gs to environmental factors. Influences of air pollutants will not be detailed, although their contribution to stomatal closure could be substantial in some conditions (see the influence of ozone, Uddling et al. 2009).
Multiplicative models of environmental influences
Some authors have integrated all or parts of the effects of environmental factors in empirical ‘multiplicative’ models. In these models, gs is the product of the response functions to individual factors, each function being generally determined by boundary line analysis (Webb 1972; Chambers et al. 1985). The hypothesis behind this approach is that the response to each environmental factor is independent of the others. Jarvis (1976) was the first to propose such a model that integrates responses to Q, leaf temperature (Tl), VPD, Ca and leaf water potential (Ψl) (Table 2; Eqn 1). A first laboratory validation concluded that this model explains 95% of the observed variation of gs.
Following Jarvis, White et al. (1999) modelled the instantaneous stomatal conductance in well-watered conditions as the product of maximal stomatal aperture (gsmax) and empirical responses to Q, Tl and VPD (Table 2; Eqn 2).
The main criticism formulated against these models was that interactive effects between environmental factors are not taken into account, although such interactions were reported, for example between VPD and Ψl (Tardieu et al. 1996).
Other authors based their approach on the principle of the existence of a limiting factor. Noe & Giersch (2004), for instance, proposed a model where gs is a function of gsmax and the minimum among two response functions to Q and VPD, respectively (Table 2; Eqn 3).
Although successfully tested in numerous circumstances, multiplicative or limiting factor-based models are essentially empirical and require new parameterization for each new environmental condition. This is their main drawback likely resulting from the assumption that environmental factors have independent effects.
Response of stomata to air humidity, transpiration rate and leaf water potential
It has been often observed that air humidity (Hr) influences stomatal aperture (Lange et al. 1971), but the way Hr is sensed by the plant remains still a matter of debate (Oren et al. 1999; Meinzer 2002; Buckley 2005). Do stomata respond to Hrper se, or to one of its correlated derivatives, that is, partial pressure of water vapour, air or leaf-to-air VPD (respectively, VPDA or VPDL), leaf transpiration rate (E) or Ψl? This section focuses on the relationship between gs and these variables. By definition, VPDA is calculated at air temperature, while VPDL is calculated at leaf temperature. From a physiological point of view, because stomatal response is driven by the local environment, VPDL is more informative than VPDA. Most authors thus consider VPDL when modelling gs. We will use the term VPD henceforth to stay faithful to the original formulation of the models presented.
Aphalo & Jarvis (1991) showed that VPD was more appropriate than Hr to describe the response of gs to humidity of the air, which makes sense considering that these variables are related by an equation derived from the diffusion equation of water vapour in the air:
where α and gb (the boundary layer conductance to water vapour) can be considered as physical parameters dependent on atmospheric pressure, temperature, wind speed and shoot architecture.
Mott & Parkhurst (1991) tried to determine whether gs responds either to humidity (partial pressure of water vapour) or E. By substituting helox for air in the atmosphere, which drastically changes gas diffusion properties, they could break the strong correlation existing between E, gs and air humidity, and thus demonstrate that stomata sense E rather than air humidity.
Following the same line, it may be argued that leaf water potential may also be substituted for E in models of stomatal response to fluctuating air humidity, because Ψl and the transpiration rate are closely linked. It may further be argued that this substitution has a mechanistic basis because it is well demonstrated that stomatal movements result from variations in leaf (or guard cell) water status, which result themselves from variations of evaporation in the substomatal cavity, and thus of the transpiration flux (see Comstock & Menuccini 1998).
Numerous relationships between gs and one of the three variables related to air humidity: VPD, E or Ψl, have been proposed in the literature. For instance, Lohammer et al. (1980) proposed a widely used hyperbolic relationship between gs and VPD (Table 2; Eqn 4). Monteith (1995) suggested to use a linear approximation of this relationship for the range of VPD commonly encountered in the field (Table 2; Eqn 5). Using Eqn 1, the linear relationship between gs and VPD can also be transformed into a linear relationship between gs and E (Monteith 1995) (Table 2; Eqn 6), provided that the boundary layer resistance gb−1 is negligible. Conditions of low wind over dense vegetation may considerably increase gb−1 compared to gs−1, and thereby distort the correlation coefficients between E, gs and VPD as given by Eqn 1. But the major problem associated with these approaches is that they rely on purely empirical parameters established in well-controlled conditions and considered as constants. Albeit very simplifying, these approaches have been widely used and proven useful in not-too-extreme conditions, generally characterized by non-limiting water supply.
Considering that stomata respond to short-term variations of guard cell water potential, some authors developed hydromechanical models, based on a precise description of water balance and turgor regulation of guard cells. Cowan (1972) first developed an electrical analogous model based on water transfer functions that explained several aspects of stomatal movements. Changes in water content with water potential of mesophyll, and subsidiary and guard cells were represented as ‘capacitors’ connected by ‘resistances’ that governed water flows. Cooke et al. (1976) then showed, using finite element shell analysis, that gs can be related to turgor pressure of guard cells and subsidiary cells (Pg and Psub, respectively) with a multilinear relationship, and not solely to the pressure difference between the two, as previously believed. The authors also theoretically demonstrated that the aperture width is more sensitive to variations in Psub than to variations of Pg, which has been proved later using the pressure probe, and was called the ‘mechanical advantage’ of epidermal cells. They also showed that it is the elliptical shape of the stomata torus that allows to properly respond to turgor pressure changes: the major axis of the torus remains almost constant, while the minor axis varies. Based on these conclusions, Delwiche & Cooke (1977) developed an analytical hydraulic model based on the dynamic behaviour of stomata. Pore area (Ast) is modelled geometrically as a function of the length of the major and the minor axes (La and Lb, respectively) (Table 2; Eqn 7). The length of the minor axis is dependent on Pg and Psub, the two variables being integrated in a system of non-linear differential equations including water potentials, turgor pressures, osmotic potentials, water vapour resistances and water fluxes of guard cells and subsidiary cells. The model suggests that hydropassive stomatal movements are insufficient to regulate water loss at low leaf water potentials. More recently, Dewar (1995) proposed a more comprehensible model of gs in which stomatal movements are governed by difference in turgor pressure between the guard cells and the bulk leaf epidermis (Pe, closely related to Psub). Turgor pressure is deduced from water potential and osmotic pressure. Stomatal response to any stimuli is then separated into: (1) a hydropassive hydraulic response based on the water potential difference between guard cells and bulk leaf epidermis (ΔΨ); and (2) a hydroactive response that involves energy-dependent osmotic regulation in guard cells (related to the osmotic potential difference between guard cells and epidermal cells, Δπ).
In Dewar's model, ΔΨ appears proportional to E by considering the hydraulic conductivity between the bulk leaf epidermis and the guard cells as a constant (Table 2; Eqn 8). As cell osmotic pressure is difficult to measure experimentally, Δπ is interpreted, by analogy to Leuning's model (Leuning 1995, see ‘Models based on a CO2 assimilation submodel’ subsection), as a function of Anet, Ci, gs and an empirical constant which is the equivalent of the a constant of Leuning's model (Table 2; Eqns 11–12). Roughly, guard cell turgor is considered to depend on the solute influx into the guard cells, and hence on CO2 assimilation rate. The analogy is not detailed here, but is discussed in section ‘Some ideas for future development’ as a possible bridge between empirical and semi-empirical models. Dewar's model introduces mechanistic bases of stomatal movements in a form easier to solve than previous proposals. However, some experimental observations are not well simulated, in particular, Dewar's model does not take into account the mechanical advantage of epidermal cells on guard cells. From a practical point of view, this model remains tricky to use, mainly because of the difficulty to estimate some parameters (e.g. k).
Ball et al. (1987) developed one of the most commonly used models of gs (abbreviated BWB model). In this model, gs responds to Anet, Hr and CO2 concentration at the leaf surface (Cs). In its original form, the model predicts that gs is equal to zero when Anet equals zero. However, a residual stomatal aperture (g0) was rapidly introduced (Table 2; Eqn 9). In the BWB model, gs dependency to temperature is indirect, via Hr (and incidentally Anet). Aphalo & Jarvis (1993) proposed an improved version of the BWB model by separating the effects of temperature and VPD (Table 2; Eqn 10).
Three main criticisms were formulated against the BWB model. Firstly, it does not simulate correctly Anet and gs when Cs equals the CO2 compensatory point (Γ). When Cs = Γ, Anet and gs should, respectively, equal zero and g0. Leuning (1990) proposed a first modified version of the BWB model by including Γ (Table 2; Eqn 11). Secondly, stomata respond to VPD rather than to Hr (Aphalo & Jarvis 1991). A second modification was proposed by Leuning (1995) which consisted in replacing Hr by the more general Lohammer's function of VPD (Lohammer et al. 1980) (Table 2; Eqn 12a). Finally, stomata do not respond directly to Csper se, but rather to Ci (Mott 1988). Anet, gs, Cs and Ci are related by the so-called supply function expressing diffusion rate of CO2 (assumed equal to Anet) across stomata (Table 2; Eqn 12b). Because Ci is unknown, the supply function must be coupled to models of photosynthetic assimilation (biochemical model of photosynthesis, e.g. Farquhar, von Caemmerer & Berry 1980) (Table 2; Eqn 12c). Either BWB or Leuning's model, coupled with the supply function, and the model of Anet form a system of three equations and three unknowns (gs, Anet and Ci), which can be solved either numerically or analytically (Baldocchi 1994).
BWB and Leuning's models (Ball et al. 1987; Leuning 1995) are still extensively used at the leaf level and may also be extrapolated at field or forest stand level (Misson et al. 2002; Alton, North & Los 2007). They are relatively easy to use and to parameterize, but they do not capture responses to soil water status. We will see in section ‘Models based on a CO2 assimilation sub-model’ that they can be modified to include those responses. These two models represent a good compromise between ease-to-use, explicative power and predictive accuracy in various experimental conditions.
Models based on a leaf photosynthetic capacity submodel
Farquhar & Wong (1984) proposed an empirical relationship relating gs to T, a parameter dependent on the concentration of ATP in the chloroplasts of the mesophyll, as a first estimate of the photosynthetic capacity. T is in turn estimated by extension of the biochemical model of photosynthesis of Farquhar et al. (1980) using ribulose bis-phosphate (RuBP) concentration and other parameters related to the photosynthetic capacity (Table 2; Eqn 13). In spite of its mechanistic basis, the model of Farquhar & Wong (1984) remains largely empirical. Moreover, it is very complex to use, particularly because of the difficulty to estimate key variables in the field (mainly RuBP concentration).
More usefully, Jarvis & Davies (1998) related gs to a ‘residual photosynthetic capacity’, the difference between actual Anet and maximal Anet when CO2 is not limiting (Amax). The authors proposed that stomatal aperture is limited by the evaporative demand (estimated by E) and the residual photosynthetic capacity (Table 2; Eqn 14). This model is easier to apply than Farquhar and Wong's (1984), but some experimental observations are not simulated correctly. In particular, positive response of gs to oxygen concentration is predicted in all conditions, while the observed response is negative in some conditions and positive in others (Buckley et al. 2003). Besides, Buckley et al. (2003) suggested that if gs actually responds to residual photosynthetic capacity, this response is mediated by a less direct variable than Anet – Amax, maybe ATP concentration in the mesophyll cells.
STOMATAL CONDUCTANCE MODELS IN THE PRESENCE OF WATER STRESS
Empirical models based on environmental factors
A simple approach to integrate the effects of water stress in gs models consists in introducing a response function to soil water deficit into the multiplicative models presented in ‘Empirical models of response to climate’. Numerous models were developed on the basis of Jarvis's model (Jarvis 1976) with a response function to soil water status replacing the response function to Ψl.
White et al. (1999) proposed a similar model using a response function to Ψpd. But, they considered that the sum of stress accumulated during a given period of time is more relevant than the current daily stress. Response functions to environmental factors are thus integrated over the considered period, and a global gs for this period can be simulated. However, the coupling with other sources of variations of gs (like Anet or E) requires instantaneous values of gs. MacFarlane, White & Adams (2004) therefore used a simplified version of White's model, where gs responds to instantaneous variations of Q, Tl and VPD on the short term, and to integrated value of Ψpd over a period of n days of stress on the long term [sum of stress, S(Ψ)] (Table 2; Eqn 17). The model well simulates field observations. As water stress effects are a combination of its strength and duration, the concept of cumulative sum of stress seems very relevant.
As said previously in ‘Multiplicative models of environmental influence’, multiplicative models present two important drawbacks: (1) they suppose that the response to each factor is independent; and (2) they require to construct response curves for each experimental condition. However, in their range of parameterization, these models can provide rather satisfactory simulations.
Specific approaches have been adopted for isohydric species (see ‘Leaf water potential and ABA’) which regulate transpiration so as to maintain Ψl constant when soil and air water status vary. For such species, Ogle & Reynolds (2002) proposed: (1) that gs regulation depends on climatic demand (estimated by VPD); and (2) that the maximal stomatal conductance (gsmax) depends on Ψpd and growth temperature (Tgro, the mean daily temperature averaged over the last 7 d). More precisely, the authors determined two empirical thresholds of VPD beyond which gs is maximal or null (Table 2; Eqn 18). The authors showed that stomatal sensibility to VPD decreases with increasing water stress. This model successfully captured the large diurnal and seasonal fluctuations of gs for a North American desert shrub Larrea tridentata. It provides accurate simulations of gs in a wide range of environmental conditions.
Models based on a CO2 assimilation submodel: modifications of BWB and Leuning's models
Water stress modifies the relationship between gs and Anet, and consequently the gs/Anet ratio (Brodribb 1996; Katul, Leuning & Oren 2003; Tuzet et al. 2003; MacFarlane et al. 2004; Misson et al. 2004; Rouhi et al. 2007). As a consequence, the models of BWB and Leuning, which are based on a linear relationship between gs and Anet, cannot properly simulate gs in water stress conditions. Numerous authors adapted these two models to water stress conditions by expressing the slope of the gs–Anet relationship relative to these models (henceforth called gbwb, gL) (Table 2; Eqns 9 and 12a) as empirical functions of plant or soil water status.
Among the first proposals, Tenhunen et al. (1990) substituted gbwb by a parameter called GFAC which has to be recalculated whenever the conditions change (Table 2; Eqn 19). More explicitly, Baldocchi (1997) introduced a cumulative drought index into gbwb. This index is a function of the sum of rainfalls divided by cumulated evapotranspiration over the considered period (Table 2; Eqn 20). Other authors proposed to modify BWB and Leuning's models by introducing a function of Ψpd. Sala & Tenhunen (1996) observed a curvilinear relationship between gbwb and Ψpd for water potentials ranging from −1 to 0 MPa, and a linear one for more negative potentials (Table 2; Eqn 21). Misson et al. (2004) introduced a power function of Ψpd into the BWB model (Table 2; Eqn 22). Wang & Leuning (1998) modified Leuning's model using a function of soil water content (θs) (Table 2; Eqn 23). Similarly, Van Wijk et al. (2000) introduced a function of θs, although of a different form, in the models of BWB and Leuning (Table 2; Eqn 24). These last authors showed that the BWB model should also be modified to include a function of Tl. For simplicity, they preferred to use the model of Leuning. More recently, Uddling et al. (2005) introduced a function of the day of the year (fseason) in Leuning's model (Table 2; Eqn 25), which integrates all seasonal effects including seasonal drought.
When available, the adjustment quality of these models, on the base of predictions versus observations regression, was reported in Table 4. R2 (the proportion of variation explained by the fitted regression) and slope deviation from unity are common measures of accuracy and bias. Equally important is the domain of validity of the model in terms of ranges of environmental conditions, level of fluctuations, species, time-scale, etc. In their original conditions of parameterization, all of the models presented in Table 4 very well simulate gs or E, even for shade leaves (Sala & Tenhunen 1996). These models do not simulate the daily variations of stomatal conductance, nor transient responses, if any, to rapid, time-varying conditions, like sunflecks. However, they may be considered as suitable for long-term water stress studies.
Table 4. Prediction quality of four modified versions of BWB or Leuning model
The approaches presented in the previous sections are based on observed relationships. With a better understanding of plant physiology, particularly of the response to water stress, models with a more mechanistic basis have been proposed.
Leaf water potential and ABA
Species differ by their degree of control of Ψl during water stress. Some species maintain Ψl almost constant during water stress (isohydric species), while others do not (anisohydric species). The gs response to ABA depends on whether the species is rather isohydric or anisohydric. For isohydric species, stomata sensibility to ABA is negatively related to Ψl. Tardieu & Davies (1993) expressed gs as a function of xylem ABA concentration and Ψl. ABA concentration is calculated from water and ABA fluxes equations within the plant (Table 2; Eqn 26). For anisohydric species, stomatal regulation in water stress conditions depends only on xylem ABA concentration (Tardieu et al. 1996). For such plants, Tardieu & Simonneau (1998) proposed to use the model of Tardieu & Davies (1993) with a δ coefficient equal to zero (see Table 2; Eqn 26). In a more straightforward manner, Gutschick & Simonneau (2002) introduced a function of ABA concentration in the xylem in the BWB model (modification of the slope of the BWB model) (Table 2; Eqn 27).
Because they depend on ABA, all these models simulate well gs in a wide range of environmental conditions, particularly for different levels of water deficit. A limitation was, however, formulated because xylem ABA concentration is commonly assessed in the sap extracted by pressurization from a shoot. This concentration is supposed to represent the average of the different concentrations inside the leaf (Tardieu & Simonneau 1998). However, from a mechanical point of view, it is the ABA concentration near the guard cells that determines stomatal closure and is expected to be correlated to gs. Because of redistribution and neosynthesis within leaves, ABA concentration measured in sap collected by pressurization can differ from ABA concentration near the guard cells. However, the simplicity of measurement of concentration in the xylem sap and the strong correlation with gs generally observed justify its use in models.
Hydraulic models are based on water transfer in the xylem, governed by thermodynamics that allows analogy to Fick's law. For a segment AB within a plant, the flux between points A and B (FAB) depends on the xylem hydraulic conductivity between these two points (KAB) and the water potential (Ψ) difference (or gradient if KAB is expressed as a conductivity and not as a conductance):
As water transfer in the xylem is conservative, in a first approximation, the water flux through the whole tree equals transpiration. Hydraulic models are then primarily transpiration models, but they can easily be converted into gs models using Eqn 1.
A first method to model gs consists in using the flux equation for the soil-to-leaf pathway. E and gs appear then as the product of the hydraulic conductivity of the soil-to-leaf pathway (Ktot) divided by leaf surface, and of the water potential gradient between the soil and the leaf. This simplified approach assumes that the plant acts as a unique pipe. It was occasionally used, for example by Oren et al. (1999), at the tree level (Table 2; Eqn 28).
However, the pipe model may arguably represent an oversimplification where heterogeneity within branches is neglected, and a more precise description of tree hydraulic architecture is then required, especially for trees. Tyree & Sperry (1988) simulated transpiration of whole trees using flux equations (Eqn 2). In their approach, the water pathway from the soil to the leaves is separated in segments that represent the tree architecture (Table 2; Eqn 29). For each segment, a specific hydraulic conductivity, estimated from its diameter, is given. The system works as an electric circuit where resistances in series and conductances in parallel may be added. Similarly, Sperry et al. (1998) decomposed the tree into different organs, from the roots to the leaves, and simulated water fluxes for each organ. They also added a precise description of water transfer from the soil to the roots. With a somewhat different approach, Tuzet et al. (2003) proposed a model of gs based on the relationship between gs and Anet, Ci, Ψl and plant hydraulic architecture (Table 2; Eqn 30). Ψl is estimated by a flux equation from the soil to the leaves that takes into account the resistances of the different segments. Actually, this model is close to a modified version of Leuning's model where the slope of the gs–Anet relationship is a function of Ψl.
In conditions of water deficit, there is a large consensus that stomatal closure controls the formation of embolism in xylem vessels through the maintenance of the xylem water potential above a critical threshold called the cavitation threshold, Ψcav. Indeed, embolism can appear when xylem water potential becomes lower than Ψcav. A last group of models are based on the hypothesis that stomatal closure controls the decrease in xylem water potential and the formation of embolism (Tyree & Sperry 1989). Jones & Sutherland (1991) simulated gs with a flux equation using the total hydraulic conductance of the plant in the soil-to-leaf pathway (Ktot). Ktot is a function of the maximal hydraulic conductivity (Kmax), and a parameter which is an estimate of the xylem embolism rate based on Ψl and Ψcav (Table 2; Eqn 31). For the authors, this formulation is adequate for cereals, while hydraulic architecture should be introduced for trees. Cochard et al. (1996a) and Lu et al. (1996) calculated a transpiration threshold (Ecrit) beyond which embolism can appear. This threshold is estimated by a flux equation at the whole-plant level, considering that xylem water potential is maintained equal to Ψcav (Table 2; Eqn 32). With the hypothesis that stomata are regulated in order to prevent embolism formation, the observed transpiration is expected to remain lower than the calculated threshold transpiration. This is observed on most species. Cochard et al. (2002) completed this approach by using a precise description of the architecture of the soil–plant–leaves continuum to estimate Ktot.
An important feature of hydraulic models is their facility of use and parameterization, which represents a serious practical advantage. They are also easy to understand as they proceed from the simple idea of the hydraulic determinism of stomatal closure. However, all these models (except Tuzet et al. 2003) focus on hydraulic mechanisms only. It is well established that various stimuli, some of which do not relate to any hydraulic control, influence gs. Thus, hydraulic models cannot be considered as universal integrative models of gs as a function of water relations.
We presented in ‘Response of stomata to air humidity, transpiration rate and leaf water potential’ a ‘hydromechanical’ model of gs, based on a precise description of water balance and turgor regulation of guard cells (Dewar 1995). This approach, primarily developed for well-watered plant, was extended to water stress conditions.
Dewar improved his model by introducing a stomatal response to leaf xylem ABA concentration (Dewar 2002). In the most recent version of this model, stomatal movements are still governed by the difference in turgor pressure between guard cells and bulk leaf epidermis (Pg − Pe), and the stomatal response is still separated into hydropassive and hydroactive responses, but the osmotic pressure difference between guard cells and epidermal cells (Δπ) is an explicit function of the quantity of ions entering the guard cells, and of the diffusion rate between guard cells and epidermal cells. This diffusion rate is estimated by the product of a minimal rate (dmin) and an exponential function of ABA concentration in the leaf xylem and of water potential of epidermal cells, formulated by Tardieu & Davies (1993) (Table 2; Eqn 33). The quantity of ions entering the guard cells not being measurable is estimated by a function of Anet, Ci and day respiration (Rd).
Using the same concepts, but by modifying one of the fundamental hypotheses, Gao et al. (2002) more precisely simulated the effects of water stress. For them, stomata do not respond to the difference in turgor pressure between the guard cells and the bulk leaf epidermis, but rather to the turgor of guard cells (Pg) (Table 2; Eqn 34); gs is then solely dependent on water potential and osmotic pressure of the guard cells (Ψg and πg, respectively). Ψg is expressed by a flux equation between the soil and the guard cells, considering the total conductivity from the soil to the guard cells (Ktot). The relationship between E, VPD and gs (Eqn 1) is then used to express gs; πg depends on the amount of assimilates in the guard cells, which is a function, in a first approximation, of photosynthesis. πg can thus be estimated from Q.
An advantage of this model compared to Dewar's model is that hydraulic components can be more easily approximated: the total conductivity from the soil to the guard cell is easier to estimate than the hydraulic conductance between bulk leaf epidermis and the guard cells. However, osmotic regulation, modelled by the diffusion of ions between the guard cells and the apoplast, is not included.
Both of these models have their advantages and drawbacks, but none of them predicts one important behaviour observed experimentally: the mechanical advantage of epidermal cells over guard cells. Buckley et al. (2003) dealt with this issue in a model similar to Gao's (Gao et al. 2002), but with the following main differences (Table 2; Eqn 35). Firstly, the epidermal mechanical advantage over the guard cells is taken into account by introducing a factor m (m > 1), which allows to weigh the effects of Pg and Pe on gs. Secondly, guard cell osmotic pressure (πg) depends on the flux of solutes resulting from the electrochemical gradient imposed by ATP synthases. πg is then expressed as a function of ATP concentration of the guard cells (semi-empirical parameter T). With the hypothesis that the same biochemical process controls ATP concentration in mesophyll and in guard cells, the guard cell ATP concentration can be simulated using the model of Farquhar & Wong (1984) (see ‘Models based on a leaf photosynthetic capacity sub-model’). Finally, the authors suggested that variations in local turgor pressure close to the guard cells are part of the signal leading to stomatal closure in conditions of water stress. πg can thus be expressed as a function of ATP concentration and Pe. Experimental evidence of the existence of a water stress sensor localized close to stomata was reviewed later by Buckley (2005).
Important features of this model have to be highlighted. Firstly, the model relates osmotic pressure to photosynthetic activity expressed by ATP content. ATP content determines RuBP regeneration activity. Thereby, gs is linked to photosynthetic activity (see ‘Models based on a leaf photosynthetic capacity sub-model’). Secondly, introducing the epidermal mechanical advantage enables to better simulate variations of gs with VPD than in the previous models, namely the transient opening with increasing VPD which results from rapid, hydropassive responses, and the subsequent closure associated with the slower, hydroactive, energy-dependent osmotic response. Moreover, ABA effects can be introduced in the model, considering that the flux of ions entering the guard cells is ABA dependent. The main drawback of this model lies in its complexity and in the important number of parameters that have to be determined.
SOME IDEAS FOR FUTURE DEVELOPMENTS
Bridges between mechanistic and empirical models
We have presented numerous models of stomatal conductance suitable for water stress conditions that can be essentially qualified from empirical to mechanistic. At this stage, all these models well simulate variations of gs in conditions of water stress.
In some cases, explicit bridges between models were proposed. Dewar presented his first model (Dewar 1995) as an improvement of Leuning's model (Leuning 1995), where the role played by turgor in the regulation of guard cell volume is clearly accounted for. As already seen in ‘Response of stomata to air humidity, transpiration rate and leaf water potential’, the osmotic gradient between guard and epidermal cells, one of the main variables of this model, was expressed as a function of Anet, Ci, gs using the empirical constant a of Leuning's model (see Dewar 1995 for the mathematical analogy). Similarly, in the second version of his model, Dewar (2002) proposed to combine the essential features of Leuning's model with those of Tardieu and Davies's (Tardieu & Davies 1993; Leuning 1995) within a common mechanistic framework. The empirical constants a and D0 of Leuning's model were expressed in terms of guard cell parameters related to hydraulic or ion transport characteristics (see Dewar 2002 for the exact expressions). The dependency of gs on ABA expressed in Tardieu and Davies's model (Tardieu & Davies 1993) was directly included into the expression of the osmotic gradient between the guard and epidermal cells (Leuning 1995; Table 2; Eqn 32).
These two models represent certainly the most advanced attempts to introduce mechanistic models into empirical ones. Such integrative approaches certainly deserve to be encouraged in the future for the potential benefits that may be derived from them. Our capacity to develop a universal, integrated and quantitative view of the effects of environmental factors with a large domain of validity probably depends on our capacity to design models built onto strong foundations, both physiological and empirical.
The issue of seasonal variations
This review presents models that cover long-term phenomena especially water stress. An important issue not discussed yet is the seasonal variations of the factors introduced in gs models. It is difficult to propose a priori laws of variation for empirical parameters. By contrast, predictive quality can be improved by incorporating pre-existing knowledge on seasonal changes in physiological factors (photosynthetic capacity and Ktot as examples). To date, seasonal variability in leaf photosynthetic capacity has been documented for only a few tree species. In tropical conditions, characterized by mild seasonal changes and non-limiting water supply, photosynthetic capacity of mango leaves appears rather stable (Urban, Montpied & Normand 2006). In contrast, photosynthetic capacity fluctuates substantially in leaves of temperate trees, as a function of either drought (Wilson, Baldocchi & Hanson 2000; Xu & Baldocchi 2003), leaf age (Wilson et al. 2000) or source–sink relationships (Walcroft et al. 2002). Observations made by Damour, Vandame & Urban (2009) suggest that the reversible decline in photosynthetic capacity of leaves from mango trees subjected to long-term drought may be attributable to the associated decrease in sink activity. The perspectives of modelling seasonal variations of photosynthetic capacity were evaluated rather positively by Damour & Urban (2007). Similarly, Ktot was shown to vary seasonally, with age (Hubbard, Bond & Ryan 1999) and environmental conditions (Cochard et al. 1996a; Lu et al. 1996). We still need to increase our understanding and develop models of the variations of Ktot as a function of these factors.
The issue of co-regulation of gs and Anet
As mentioned previously (section ‘Models relating gs to photosynthesis’), the most used models of gs, namely the models of BWB and Leuning, are based on the concept of Ci homeostasis which implicitly assumes a stable ratio between water consumption and carbon gain (WUE). They consequently exploit the idea that the gs-to-Anet ratio is a constant in conditions characterized by non-limiting water availability and in the absence of limitations imposed by either carbohydrate accumulation or reduced sink activity. While easy to comprehend in a deterministic perspective, a constant gs-to-Anet ratio appears more difficult to explain mechanistically. Stable Ci may result from the source-to-sink balance for CO2 fluxes. A decrease in gs lowers Ci and hence Anet because less CO2 enters the leaves. The decrease in Anet tends in turn to increase Ci because less CO2 is consumed, which eventually results in a more or less stable Ci. Alternatively, it has been suggested that a direct feedback control of gs by Ci is at the origin of the relative maintenance of Ci. However, the gs response to Ci appears too weak to permit such a feedback (Sharkey & Raschke 1981). More recent works suggest that part of the response of gs to Ci (or red light) is linked to photosynthetic electron transport (Messinger, Buckley & Mott 2006), which provides a mechanistic basis for the gs–Anet relationship. The nature of the mediator remains unknown, but some evidence locates it in the mesophyll (Mott 2009). Moreover, considering that ABA inhibits several enzymes of the Calvin cycle (Rook et al. 2006), it is tempting to hypothesize that ABA co-regulates both gs and Anet, and to use [ABA] for modelling both gs (Tardieu & Davies 1993) and Anet.
However, there are conditions where either a constant Ci or gs-to-Anet ratio is not observed. In particular, it has been repeatedly observed that the gs-to-Anet ratio shifts in drought conditions (Brodribb 1996; Lawlor & Cornic 2002; Medrano et al. 2002; Katul et al. 2003; MacFarlane et al. 2004; Urban et al. 2006; Damour, Vandame & Urban 2008), which seriously limits the generalization of the use of several models of gs and Anet. Similarly, it has been observed that carbohydrate accumulation or reduced sink activity not only reduces Anet, but also gs, that may result in shifts in the gs-to-Anet ratio (Urban & Alphonsout 2007; Duan et al. 2008; Wu et al. 2008). Moreover, both issues are possibly linked: it has been suggested that the long-term negative effect of drought on Anet may be interpreted as the consequence not only of reduced gs and Ci, but also of reduced sink activity relative to sources and subsequently of altered photosynthetic capacity (Damour et al. 2009). All these observations suggest that the relationship between gs and Anet is a complex one, and that simple conceptions based on a reciprocal influence through Ci or co-regulation by ABA are not totally satisfying. However, these observations reinforce the idea that gs responds to the balance between photosynthetic electron transport and carbon reduction (Messinger et al. 2006; Mott 2009).
The coupling of gs models with CO2 assimilation submodels raises questions on which factors control Anet and how they can be influenced by water stress. As discussed above (section ‘Models based on a CO2 assimilation sub-model’), Anet submodels incorporate effects of air humidity and temperature, light intensity and biochemical characteristics on the one hand, and of Ci on the other hand, which depends itself on gs. It has been much debated whether Anet limitation by drought is of diffusive (stomatal) or biochemical (non-stomatal) origin. The answer clearly depends on drought intensity and duration (see e.g. Grassi & Magnani 2005). Most studies have been biased by the underestimation of the diffusive resistance to CO2 beyond stomata, within the mesophyll, that uncouples Ci from CO2 concentration in chloroplast, where assimilation operates (Flexas et al. 2008). It is now established that diffusive limitations are much more important than biochemical limitation in conditions of mild water deficit (Keenan, Sabate & Gracia 2010). Better understanding of the way water stress reduces mesophyll conductance to CO2 should help in quantifying its role and precising the conditions when models should incorporate effects of water stress on either mesophyll and/or biochemical parameters.
Including hydrogen peroxide in models of gs
Current molecular models of guard cells functioning have not been exploited so far in the perspective of mathematical modelling of gs, although they may provide some useful ideas. In the recent past, it has been established that ROS are essential signalling molecules that mediate ABA-induced stomatal closure and ABA-induced inhibition of stomatal opening (Yan et al. 2007). This is consistent with the current view of the crosstalk existing between the signalling pathways involving ROS and phytohormones in the control they exert on plant stress responses (Fujita et al. 2006). Among all ROS, hydrogen peroxide (H2O2) emerges as the most important one considering its role in guard cell functioning and more specifically in the guard cell ABA-signalling network (Pei et al. 2000; Schroeder et al. 2001; Wang & Song 2008). The emerging view is one of great complexity, and there is certainly a challenging task ahead for elucidating the signalling networks in guard cells for ABA and H2O2. Meanwhile, it may appear tempting to try to design models of gs using H2O2 as one major entry parameter besides Anet and [ABA]. In addition to its leading role in the control of guard cell movements besides and in conjunction with ABA, there are several arguments in favour of using H2O2 in future physiologically based models of gs.
Firstly, H2O2 concentration may provide an essential and complementary link between gs and Anet, in addition to Ci and [ABA], which has been largely ignored so far in gs models. The production of ROS in plants is ascribed to several potential sources, but photosynthesis represents the major one in plants (Asada 1999). A decrease in photosynthesis, or, more precisely, an increase in the imbalance between the energy entering under the form of photons and the energy used by photochemistry, like the one resulting from a decrease in gs and CO2 supply, increases the probability of production of ROS, and especially H2O2 (Grassmann, Hippeli & Elstner 2002). Interestingly, not only gs and Anet are influencing each other through [H2O2], but also [H2O2] may co-regulate gs and Anet, because it has been observed that H2O2 inhibits several enzymes of the Calvin cycle (e.g. the FBPase; Charles & Halliwel 1981).
Secondly, H2O2 production represents the converging point of several environmental factors known to influence gs in addition to drought, such as UV radiation and sugar accumulation in leaves, the latter resulting from either reduced sink activity or elevated CO2, because these factors are known to favour oxidative stress in leaves. H2O2 arguably provides an opportunity to integrate into models of gs, the influence of environmental factors that were discarded until now and that we absolutely need to consider as part of the issue of global change. For instance, UV-B radiations are expected to increase in the coming years and have been observed to reduce gs (Paoletti 2005; Poulson, Boeger & Donahue 2006). UV-B radiations are known to favour ROS generation through their stimulating effects on peroxidases and NADPH oxidase. More specifically, it was observed that UV-B modifies H2O2 and nitric oxide generation in guard cells (He et al. 2005). It may thus be hypothesized that UV-B stimulates stomatal closure via the guard cell response to H2O2. Atmospheric CO2 concentration is predicted to increase up to threefold since 2050 (IPCC 2007). Stomata of most species close in response to elevated CO2 concentration (Moore et al. 1999; Rogers et al. 2004; Ainsworth & Rogers 2007). But, elevated CO2 increases photosynthetic rate in the short term, while photosynthetic capacity is down-regulated in the medium/long term (Moore et al. 1999; Rogers et al. 2004; Aranjuelo et al. 2005; Ainsworth & Rogers 2007; Erice et al. 2007). Because of its potential impact on photo-oxidative stress, the short-term effects of elevated CO2 could be included in H2O2-based models of gs. More generally, these observations are strong incentives in favour of more mechanistic approaches for gs modelling, more specifically when there is a need to operate outside their empirical domain of construction, as imposed in the context of global changes.
Thirdly, H2O2 production may lend itself to modelling. Noctor et al. (2002) has suggested that H2O2 production can be modelled as a function of irradiance. Of course, such a model would have to be refined by including the exacerbating effect of sugar accumulation in leaves or sink limitation (Urban & Alphonsout 2007). Coupling models of gs with models of carbon assimilation and carbohydrate repartition certainly represents an important objective as part of such an approach. Ideally, one should also include the effects of the scavenging enzymes or enzymatic systems. The rates of production of NADPH and of regeneration of ascorbate probably play an important role here. At this stage, there is no model of either ROS concentration or cell redox status that could be exploited. So, it will certainly be necessary to start by designing models of H2O2 concentration based on simplifying hypotheses before integrating them in gs models.
A model of co-regulation of gs and Anet, including the pathways presented in this section, is proposed in Fig. 1.
Other issues associated with the global change
In the context of global change, factors that appeared previously as minor become very important and require to be fully integrated into models (Xu & Baldocchi 2003). This is clearly the case of temperature. As air temperature is predicted to increase by a few degrees, stomatal conductance will be strongly affected (Jarvis 1976; Jones 1992). It is generally expected that gs will globally decrease as the consequence of the increase in air temperature. Leaf temperature will increase more than expected as the consequence of the increased air temperature because of reduced cooling by transpiration when stomata close. This increase in leaf temperature will be even more marked in conditions of drought because of the negative effect of drought on gs. Eventually, photosynthesis will be strongly reduced. That is not all: a synergetic effect between high temperature and elevated CO2 elevation has been reported, which results in down-regulation of photosynthetic capacity (Erice et al. 2007). So far, models of gs are not capable to integrate the combined effect of the simultaneous increase in air temperature, CO2 concentration of the air and drought.
Models of gs have eluded so far the question of the morphology-mediated effect of drought on gs. In response to environmental stresses, modifications of the morphology of the plant were reported. It was observed that drought results in: (1) a decrease in the specific leaf area that leads in turn to a decrease of the evaporative surface (Assuero et al. 2002; Gomez-Del-Campo et al. 2003; Al-Khalifah et al. 2006); (2) a decrease of the number of leaves on new shoots (Gomez-Del-Campo et al. 2003) and abscission of existing leaves (Gu et al. 2007); (3) an increase in the root-to-shoot ratio (Assuero et al. 2002); and (4) modifications in vessel anatomy that favour small diameter vessels (Al-Khalifah et al. 2006). These adaptive strategies buffer the effects of water stress on gs and, for that reason, should be integrated into models. An attractive way to achieve that should be to introduce whole-plant changes into a model of gs. Here are some avenue of research: (1) intercepted light as affected by leaf area; (2) photosynthetic capacity as affected by root-to-shoot ratio; and (3) hydraulic resistance as affected by vessel anatomy (Buckley 2008).
Modelling gs represents a major objective and challenge for the scientific community. What is at stake in the long term is the capacity to develop an integrated view of the way interactive environmental factors influence, either directly or indirectly, carbon fixation by photosynthesis and water losses through transpiration. The capacity to develop such an integrated view conditions in turn our capacity to design models of gs which can be used, among other objectives, for simulating the consequences of the climatic change. Roughly, two major types of models have been developed so far: models expressing gs as a function of atmospheric factors, and models expressing gs as a function of water availability. Considerable efforts have been made to design models of gs of more universal value, capable to deal simultaneously with all the environmental factors. Arguably, the most advanced of them are based on the well-established role of ABA in the control of the movements of guard cells. Considering the recent advances in our understanding of the molecular bases of stomatal regulation, we advocate for the use of H2O2 production in addition and in conjunction with ABA concentration in future models of gs. This should facilitate the integration of such factors as UV radiations and long-term drought, which have been more or less ignored by current models of gs. With the same objective in mind (i.e. integrating better the complex influences of environmental factors, especially the ones associated with the global change), it would be stimulating to explore other ideas originating from the emerging molecular view of stomatal regulation. For instance, it is now well established that aquaporins play a key role in water relations and stomatal regulation (Tyerman et al. 1999; Johansson et al. 2000). Their regulation in response to environmental stresses opens promising perspectives, particularly in modelling.
While the progressive construction of a more and more complete view of stomatal regulation at the molecular level represents a source of novel ideas for the modeller, conversely the need to design more performing models of gs represents a clear incentive for more fundamental research to be performed about the physiological determinism of guard cell functioning. Clearly, both approaches should greatly benefit from each other.
We thank the two reviewers who gave important comments and helped to complete this review. G.D. acknowledges support from the Conseil Régional de la Réunion (PhD grant) and from the CIRAD. T.S. acknowledges support from the French Agence Nationale de la Recherche grant ANR-06-BLAN-0122.