Climate-related studies have generally focussed upon physiologically well-defined ‘mechanistic’ traits rather than ‘functional’ ones relating indirectly to resource capture. Nevertheless, field responses to climate are likely to typically include both ‘mechanistic’ specialization to climatic extremes and ‘functional’ strategies that optimize resource acquisition during less climatically-severe periods. Here, this hypothesis was tested. Seventeen traits (six ‘functional’, six ‘mechanistic’ and five ‘intermediate’) were measured from 19 populations of oleaster (wild olive) along a climatic gradient in Morocco. Principal components analysis of the trait dataset identified size and the ‘worldwide leaf economics spectrum’ as PCA axes 1 and 2. However, contrary to our prediction, these axes, and commonly-measured ‘functional’ traits, were little correlated with climate. Instead, PCA 3, perhaps relating to water-use and succulence, together stomatal density, specific leaf water content and leaf shape, patterned with altitude, aridity, rainfall and temperature. We concluded that, at least for slow-growing species, such as oleaster, ‘mechanistic’ traits are key to identifying mechanisms of climatic restriction. Meaningful collaboration between ‘mechanistic’ and ‘functional’ disciplines provides the best way of improving our understanding of the global impacts of climate change on species distribution and performance.
Citation: Kassout J, Terral J-F, Hodgson JG, Ater M (2019) Trait-based plant ecology a flawed tool in climate studies? The leaf traits of wild olive that pattern with climate are not those routinely measured. PLoS ONE 14(7): e0219908. https://doi.org/10.1371/journal.pone.0219908
Editor: Khawaja Shafique Ahmad, University of Poonch Rawalakot, PAKISTAN
Received: March 8, 2019; Accepted: July 4, 2019; Published: July 17, 2019
Copyright: © 2019 Kassout et al. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Data Availability: All relevant data are within the manuscript and its Supporting Information files.
Funding: This research was supported by EcoGenOlea (2015-2017), Toubkal grants (15/04, n°32525WH) and the Moroccan Excellency research grants (024UAE2014).
Competing interests: The authors have declared that no competing interests exist.
There is a long tradition of studying characteristics of the plant phenotype (traits) that determine how plants respond to environmental factors [1,2]. The measurement of functional (adaptive) traits along environmental gradients has led to the identification of recurrent syndromes of co-occurring plant functional traits or ‘plant functional types’ particularly in relation to resource capture and allocation. These ‘plant functional types’, are a consequence of trade-offs, where traits that facilitate the exploitation of one environment simultaneously reduce fitness in another and, for many, their functional significance is underpinned by ecological theory. In this context, arguably the most fundamental and over-arching set of ecological rules relating plant performance to the environment is provided by CSR strategy theory [3,4]. CSR strategy theory defines two groups of environmental factors that vitally impact upon plant performance. The first, stress (S), includes factors that restrict plant production, particularly mineral nutrients. Other stress factors include suboptimal temperatures and a shortage of light or water. The second group, disturbance (R), results in the destruction of already-produced plant biomass, promoting ruderal growth. Disturbance may result both from the impacts of land use and from extreme climatic events. Where, stress and disturbance are both low, the distribution of species is determined by a third factor, between-plant competition (C). Nevertheless, to date, the use of functional traits has concentrated upon just two areas within strategy theory. The first is the ‘worldwide leaf economics spectrum’, a major factor within stress sensu Grime . This separates species of fertile habitats from those of unproductive ones [5,6]. It is defined both within the classical definition of relative growth rate by Evans  and by a fundamental trade-off in leaves between the rapid acquisition of nutrients and the conservation of resources within well-protected tissues [8–11]. The second much-studied topic within strategy theory is plant size. The expression of size is a complex function of the qualitative and temporal opportunities for growth controlled by environmental factors and by interactions with other plants (i.e. combinations of competition, disturbance and stress; Grime ). As a consequence of this choice of traits, global meta-analysis within mainstream trait-based plant ecology [12,13] simply identify the ‘worldwide leaf economics spectrum’ and plant size as the two key axes of specialization. Nevertheless, studies of this type, often called ‘trait-based plant ecology’, have been advanced as a key discipline for understanding and advising upon global processes of ecosystem change . A great strength of trait-based plant ecology is that the attributes routinely targeted can be both of ecological significance and easily measured. Numerous species, or even whole floras can be easily categorized with respect to many contrasted ecological dimensions. Moreover, the approach has already been used to compile large and varied trait databases . Encouragingly for the future, many additional traits are available for study  and their use may further broaden the scope and utility of trait-based plant ecology.
Intraspecific variation in trait expression–small changes with large impacts?
To date trait-based plant ecology has primarily focused upon interspecific comparisons [5,15]. In contrast, intraspecific traits, while often equally ecologically significant, have remained comparatively neglected [16–19]. This is unfortunate. As in interspecific comparisons, intraspecific traits frequently pattern instructively along environmental gradients [20,21]. Moreover, intraspecific differences may equal or even exceed those from interspecific studies [22,23]. They are also potentially relevant to climate studies (e.g. tolerance of water stress ) as well as, to more general investigations of species coexistence and distribution . These similarities with studies of interspecific traits do not, however, by themselves make a strong case for more intraspecific investigations. However, additionally, and importantly, not all species have the same ecological impact. Amongst, those of greatest ecological significance are canopy dominants, sometimes called ‘ecosystem engineers’ [26,27]. These species monopolize primary resources and, as a result, have a major impact on the ecological functioning of the whole community [26,27]. In order to accommodate these and similar species, we, like Fajardo and Piper , Bolnick et al. , Albert et al. , Laforest-Lapointe et al. , Moran et al. , Shipley et al. , believe that change is needed. An intraspecific dimension should be routinely factored into global models.
Studying climate–a methodological dilemma
Despite its long-appreciated importance , our capacity to predict the potential impacts of climate change upon the world’s flora remains constrained by problems of ecological complexity [33–35]. Moreover, within the context of climate studies the 'functional trait’ approach described above has so far failed to identify and quantify mechanisms of climatic restriction. The most highly-cited paper  simply asks the important but preliminary question ‘Which is the better predictor of plant traits, temperature or precipitation?’ More recently, global correlations between traits and climatic variables have also been used to predict possible impacts of climate change on biomass yield . In contrast, an alternative overtly ecophysiological approach has greatly increased our understanding of the impacts of climate on plant performance and survival. Through experimentation, syndromes of ‘mechanistic’ traits conferring tolerance of defined climatic factors have been identified with their function directly interpreted in terms of physics and chemistry. For example, thermal response time of the leaf to changes in surface energy fluxes has been recognized as a major component of physiological tolerance to drought [38,39]. Thermal response time is critical to leaf carbon economics and is defined by leaf traits such as dry matter mass, water mass, specific heat capacity, surface area, width, shape and stomatal density . Similarly, the characteristics of the plant’s hydraulic system additionally regulate response to climate [40,41]. Here, key traits include leaf water potential at turgor-loss point, plant hydraulic conductance or xylem vulnerability [42–44] and, more generally, root architecture [45,46]. Furthermore, encouragingly, Brodribb  outlines how simple ‘mechanistic’ traits identified in ecophysiological studies define hydraulic physiology and may be used to explain and predict climatic restriction due to drought.
The contrast between the relatively climatically ineffectual ‘functional’ traits and the more ecophysiologically insightful ‘mechanistic’ traits has catalysed a debate as to how best to advance our understanding of plant-climate interactions . Provocatively, Brodribb writes: ‘By ‘mechanistic’ traits, I mean traits whose function can be clearly physiologically defined, as opposed to the more abstract ‘functional’ traits, such as leaf mass per area (LMA, also known as specific leaf area (SLA)), that have been used to great effect in explaining plant economics over the last 15 years ’. Brodribb’s subdivision has been re-enforced by Volaire . Volaire separates ‘mechanistic’ traits as physiological strategies relating to one dominant environmental factor and studied explicitly over short timescales from ‘functional’ traits with ecological strategies relating to multi- environmental factors and studied implicitly over long timescales. However, this debate ignores a key point. ‘Mechanistic’ studies are time-consuming and most include few species. They provide precision in measurement but the general significance of each mechanism at a global scale is more difficult to study because inevitably datasets are small. In contrast, as outlined above, the ‘functional trait’ approach can quickly generate large datasets for whole floras with each species defined in many contrasted ecological dimensions. As in other comparative approaches the ‘functional trait’ approach has a strong potential for generality. ‘The collection and comparison of standardized information …… follows closely the philosophies prevailing in the physical sciences. Perhaps the most obvious of these is the role played by the Periodic Table of the Elements in classifying, analysing, and even predicting, the structure and properties of chemical elements and compounds’ . Why has the ‘functional trait’ approach had so little impact on understanding the role of climate on plant distribution? The failure appears to stem from the consistent use of a restricted and ‘climatically inappropriate’ set of traits. Traits linked to ‘mechanistic’ climate-related studies are conspicuously absent from ‘functional’ analyses both in studies describing general global patterns of specialization [12,13] and in those with a more climatic focus [36,37]. A plethora of potentially important climate-related traits still require further investigation. With interdisciplinary collaboration, the ‘functional trait’ approach has the potential to add important elements of generality and utility to the current pioneering ‘mechanistic’ studies …. provided, of course, that suitable, easily- and rapidly-measurable traits can be borrowed from the existing raft of ‘mechanistic’ studies.
Our trait-based study will focus upon climate and, in particular, oleaster, or wild olive, growing along a climatic gradient in Mediterranean Morocco. Both species and region are of climatic relevance and interest. Climate change is predicted to increase the geographical range of the olive . Equally, the Mediterranean region is both a biodiversity hotspot  and under severe threat from climate change [52,53]. Specifically, variation in trait expression will be explored between and within nineteen populations of oleaster from climatically-contrasted habitats. The traits to be measured fall into two groups. The first group comprises ‘functional traits’, attributes that identify the ‘worldwide leaf economics spectrum’ and plant size. These traits are essentially those routinely measured in ‘functional’ studies. The second group includes ‘mechanistic’ traits linked to climate by physiological studies but not currently used in most ‘functional trait’ studies. Of necessity, we will concentrate attention on ‘mechanistic’ traits that may be measured rapidly. We shall assess both individually and in combination, which traits pattern more exactly with climatic variables, (a) ‘functional’ or (b) ‘ecophysiological’ traits. In this context, we suggest that field responses to climate has two components (Fig 1). First, ‘functional’ strategies relating to the ‘leaf economics spectrum’ may be expected to optimize resource acquisition and growth during less climatically-severe periods. Secondly, ‘mechanistic’ strategies involving ‘ecophysiological traits’ linked to climate by physiological studies will confer tolerance of climatic extremes. Since oleaster is both slow-growing and long-lived tree, survival of climatic extremes will be key. Accordingly, our specific hypothesis is that, for oleaster, ‘ecophysiological traits’ little-used in trait-based plant ecology will pattern with climatic variables more effectively than commonly-used ‘functional traits’. More generally, we suspect that ‘functional’ trait-based plant ecology will have little impact on climate change research until it routinely includes a ‘mechanistic’ dimension to its trait measurements and analyses.
‘Mechanistic’, relating particularly to specializations for surviving harsh climates, and ‘functional’ traits sensu Broderibb , that may optimize growth during other periods, are coloured blue and red respectively. ● identifies the putative position of Olea designated with a orange color.
Materials and methods
Oleaster (Olea europaea subsp. europaea var. sylvestris (Miller) Lehr) is the wild progenitor of the Mediterranean cultivated olive (Olea europaea L. subsp. europaea var. europaea) (Besnard et al.  for review). It is an evergreen, sclerophyllous, long-lived wind-pollinated tree [55–59]. Oleaster is a characteristic component of the natural Mediterranean vegetation [60,61] and its presence may be traced back to at least the last glaciation period [61–63]. It is considered a bio-indicator of the Mediterranean climate [61,64–67] and arguably the most emblematic and iconic tree of the Mediterranean Basin . In Morocco climax vegetation with oleaster extends over several Mediterranean bioclimates from humid to arid along a north-south latitudinal gradient and oleaster appears eliminated mainly by the cold (maximum altitude between 1000 and 1600 m) and extreme aridity . Because of its importance, (a) in climate studies, as a bio-indicator, and (b) in studies of ecosystem function, as a major component of the vegetation, oleaster is an ideal species for studying traits along a climatic gradient.
The field context was provided by a 600 km latitudinal transect of Morocco that includes a wide range of habitats and vegetation types across three bioclimatic zones (humid, subhumid and semi-arid) within Morocco (Fig 2) [68–73]. We chose nineteen representative woodland and scrub sites each with contrasted climatic, geographical and phytoecological characteristics (Table 1). The climate of each site was defined using five variables: mean annual temperature (MAT,°C), minimum temperature of the coldest month (MTCM, °C), and the mean annual precipitation (MAP, mm), all extracted from the Worldclim database, at a resolution of 30 arc’s (~1 km2)  plus the mean annual evapotranspiration (PET, mm/year) and the global aridity index (AI, unitless, calculated as MAP/PET) from, respectively, the PET database and the CGIAR Global Aridity database [75,76]. The range of climate associated with our sites (Table 1) is greater than changes to climatic variables predicted by Gibelin and Déqué  and Polade et al.  making our study area more relevant to climate change research.
Site numbers accord with Table 1.
Sampling in the field requires no authorization; the study sites are located in natural public areas outside protected natural areas. The species studied (Olea europaea subsp. europea sylvestris (Miller) Lehr) is not a rare or protected species.
At each site, ten healthy oleaster trees were randomly selected from within of a 200m2 area during the spring (April to May) of 2016. The diameter at breast height (DBH) and the vegetative height (H) of each tree were recorded as proscribed by Bonham . Subsequently, relative chlorophyll content (CHL, SPAD units) was measured using a SPAD 502 plus chlorophyll meter and following the protocols of Cornelissen et al. , thirty healthy, mature leaves were collected at random from the south (sun-exposed) side of the upper canopy and returned to the laboratory on the day of sampling in a cool, hydrated condition.
Seventeen plant traits were measured (Table 2). Six were ‘functional’ traits, relating to size or to the ‘leaf economics spectrum’, of the type more traditionally used in trait-based ecological studies. We are trialing a further six ‘mechanistic’ traits identified from the physiological literature as of possible relevance in climate studies. Additionally, five ‘intermediate’ traits were included. These were potentially relevant to both resource capture and to climate. Traits were further categorized into four inexact groupings relating to what was being measured: (1) ‘ecophysiological’, both function and measurement relating to one component of leaf form and function (e.g. stomatal density (DS)); (2) ‘morphological size and shape’, both function and measurement relating to the whole leaf (e.g. leaf area (LA)), (3) ‘structural allocation’, function estimated from interacting properties of the whole leaf (e.g. specific leaf area (SLA)) and (4) whole plant (e.g. plant height, m; H). Group 1 is analogous to ‘mechanistic’ in so far as there is a relatively precise and direct connection between how the trait functions and what was measured. Also groups 3–4 equate to ‘functional’ traits and group 2 may be viewed as intermediate, with impacts upon both growth and water use efficiency. As a matter of policy, we have opted to concentrate on traits that may be measured quickly and easily. Such traits may be more readily incorporated into trait-based ecological studies.
For each leaf trait there were 30 replicate leaves tree-1 x 10 trees site-1 x 19 sites, making a total of 5700 replicate leaves. Trichomes were removed from the abaxial leaf surface of Olea, a hypostomatous species and impressions made using clear nail polish [83,84]. Subsequently, stomatal density (DS, no. of stomata mm-2) was measured from four separate areas of the abaxial surface of the leaf at 400x magnification (Olympus BX43). Additional laboratory- measured traits were–group 1: leaf water content (LWC, g; LWM–LDM), specific leaf water content (SLWC, g cm-2; (LWM–LDM)/LA) ), leaf thickness (LT, mm, using a precision micrometer (Mitutoyo, 0,01-25mm)); group 2: leaf area (LA, cm2), length (LL, cm), width (LW, cm), length of the broadest leaf (LLmax, cm), two estimates of leaf shape length:width ratio (LL/LW) and length: longest length ratio (LL/LLmax), [86,87]; group 3: leaf fresh mass (LWM, mg), leaf dry mass (LDM, mg), specific leaf area (SLA, cm2 g-1; LA/LDM); leaf dry matter content (LDMC mg g-1, LDM/LWM). In addition, the functional syndrome, CSR-strategy, was calculated from leaf traits by the method of Pierce et al. .
After checking frequency distributions for normality and variance heterogeneity, it was necessary to log-transform trait values prior to analysis. Subsequently, one-way ANOVA with Tukey HSD post hoc tests, Pearson correlations and principal component analyses (PCA) were undertaken for inter-population comparisons of trait values and of coefficient of variation (CV) estimates using the open source statistical environment R 3.3.3 .
Intraspecific variation of the 5700 replicates for each leaf trait was explored across three levels of spatial and organizational scales: 1) ‘regional’, between different sites; 2) ‘population’, between different trees at same site, and 3) ‘individual’, between leaves on the same tree (Fig 3). Here, the coefficient of variation (CV), calculated by the formula CV (%) = standard deviationtrait/meantrait x 100 , evaluates the amplitude of trait variability [112,113]. This is particularly true where there is a proportionality between the mean and standard deviation of the distribution . The ‘varcomp’ function in the ‘ape’ package extracted these variance components  and to quantify the extent and importance of variance across regional, population and individual scales, a general linear mixed model was fitted using the restricted maximum likelihood (RMEL) method, a nested ANOVA with random effects . Subsequently, the Canberra metric (CM) calculated as: CM = (CVmax−CVmin)/(CVmax + CVmin) tested for significant differences between the two coefficients of variation [116–118]. When the value of CM is higher than 0.1, differences are considered significant.
Ecological relevance of coefficients of variation (CV) values
Mean and standard deviation for all measured leaf traits differed markedly in their amplitude of variation. Nevertheless, apart from DS, both were significantly correlated (X v σ calculations in Tables 3, 4, 5 and 6, S1 Table). Moreover, CV values generally did not vary in the same direction as the variance ratio, F. Thus, for example, LT had a low CV value (21%) but high F value and appeared strongly discriminant between populations (Table 3). Also, values for the Canberra metric (0.19 to 0.69; S1 Table) exceeded the 0.1 threshold for statistical significance. Our more extreme inter-population differences in CV for each traits may be viewed as both statistically and potentially ecologically significant.
Variation in trait expression between and within populations
For each trait studied, statistically significant differences were detected between populations and for all but one of their CV values (Tables 3, 4, 5 and 6). The size of the variance ratio, F, differed considerably and traits with the highest value of F in Tables 3, 4, 5 and 6 also exhibited more of their percentage variance at the highest hierarchical level (i.e. between populations; Table 7). Thus, with the exception of CHL, ‘ecophysiological’ leaf traits, mostly classified as ‘mechanistic’, had a higher value for the variance ratio than those relating to ‘morphological size and shape’ and to ‘structural allocation’ (Tables 3, 4 and 5). They also contained 50 to 80 percent of the total variance ‘between populations’ (Table 4). At the opposite end of the spectrum were LDMC and SLA, two key ‘functional’ traits in the ‘worldwide leaf economics spectrum’ , and LL/LLmax. These traits appeared inherently plastic, with 48 to 61 percent variance between leaves on the same tree. A majority of morphological traits (LA, LL, LLmax, LL/LW) were intermediate with the percentage variance slightly higher at the ‘population’ level (42–48%). For the remainder, variance in trait expression was distributed relatively evenly between the three hierarchical levels.
Interrelationships between traits and the identification of syndromes of co-occurring traits
Correlation matrices for the traits and for their CV values are presented as Table 8 and S2 Table, respectively. Correlations between traits (Table 8) ranged in number (and percentage) from CHL (0, 0%) to, at the other extreme, DBH (9, 53%), with SLA (6, 35%) and LDMC (7, 41%). The mean number of correlations with other traits ± standard deviation could be roughly ordered as: ‘ecophysiological’ [‘mechanistic’] (4.0 ± 3.3, n = 5) < ‘morphological’ [‘intermediate’] (5.7 ± 2.5, n = 6) < ‘structural’ [‘functional’] (7.0 ± 0.8, n = 4) = ‘whole plant’ [‘functional’] (6.5 ± 3.5, n = 2). Fewer statistically significant relationships were detected in the correlation matrix for CV values and of these, a disproportionately high 40 percent related to ‘structural’ traits including SLA and LDMC (S2 Table).
Site 13 (Moulay Bouazza) with exceptionally high values for LWC, SLWC and LT has been excluded from this and subsequent analyses.
With regard to estimates of CSR strategy, which is described in the Introduction, populations were classified variously as stress-tolerant competitors (SC) and as intermediate between this strategy and stress-tolerators (S/SC), with percentage values ranging from 9–19 for the competitive (C) dimension, 81–91 for stress-tolerance (S) and consistently zero for ruderality (R; Table 6). In the PCA analyses of traits (Table 9) axis 1 identified size and was positively correlated with plant dimensions (DBH, H) and a plethora of size-related leaf traits (LA, LL, LLmax, LW, LWC, LWM, LDM). Axis 2 included aspects of the ‘worldwide leaf economics spectrum’ [5,6] with LT and LDMC (both positively) and SLA (negatively) impacting upon the expression of the axis. High values on axis 3 was identified by small leaves (LL–), a high water content (SLWC+), high leaf construction costs (SLA–) and low stomatal density (DS–). We need to investigate whether trait expression in site 13, a functional outlier, excluded from the analyses because of its high values for LT (value 125% that of the next highest site average; Table 3), LWC (>300%) and SLWC (>400%), is influenced by similar factors to those defining this axis. The PCA analysis for traits plus CV values, included for completeness as S3 Table, generated broadly similar results.
Correlates with climate
Each site has its own characteristic climatic regime (Table 1). As a result, for a canopy dominant such as oleaster, traits that pattern most strongly with site are also more likely to pattern with climate. Consistent with this, the traits that varied most between sites (with the suffix s) had the greatest percentage of statistically significant correlations with climatic indices (45%; Table 10A). These traits were classified as ecophysiological/’mechanistic’. In contrast, for traits where more variance was expressed within the same population (morphological/‘intermediate’, t) or between leaves on the same tree (leaf/‘functional’, l), the percentage of statistically significant correlations was lower (25% and 6% respectively; Table 10A).
The traits most consistently correlated with climate were DS and leaf shape (LL/LW), negatively, and SLWC, positively correlated with mean annual precipitation (MAP), minimum temperature of the coldest month (MTCM), global aridity index (AI) and Altitude (Table 10A). The only trait significantly correlated with mean annual temperature (MAT) was DS (Table 10A). Importantly, SLA, a ‘flagship’ trait in both the ‘leaf economics spectrum’ and, more generally, in trait-based plant ecology, was one of the traits not correlated directly with any of the climatic variables.
Of the syndromes of traits, PCA axis 3, which explained only 12% of the variation in the dataset (Table 9), was correlated with all five climatic-related variables (Table 10A). In addition, PCA axis 2 patterned with MTCM and AI. However, PCA axis 1 and CSR strategies showed no significant correlations. Moreover, the additional inclusion of CV in PCA analyses axes reduced rather than enhanced the extent of correlation with climatic variables (S3 Table) and in separate analyses of CV values only the traits LL/LLmax, LDMC and CHL were frequently correlated with climate (Table 10B).
The traits and trait syndromes that pattern with climate± and those that don’t
A basic premise in much of trait-based ecology is that taxa may be grouped using physiological and morphological traits into functional types, with taxa in the same functional group displaying similar responses to the environment [119,120]. Consistent with this, major PCA analyses of the world flora have routinely identified two key dimensions of functional specialization, the ‘worldwide leaf economics spectrum’ and size [12,13]. Here, for populations within a single species, oleaster, we confirm these generalities. Axes 1 and 2 in our PCA analysis are analogous with the same two axes recognized in global studies (Tables 3–10). However, these axes did not consistently pattern with climatic variables. Instead, a further ‘climatic’ PCA axis 3, was identified defined primarily in terms of ecophysiological/’mechanistic’ leaf traits (Table 10A). Equally, a majority of the statistically significant correlations between individual traits and climate included ecophysiological/’mechanistic’ leaf traits rather than the more commonly used structural/‘functional’ ones (Table 10A). However, a precise interpretation in terms of ecological processes is not yet feasible. Both the origin and the generality of variability in trait expression are in need of further study. Oleaster is slow-growing and long-lived [56,59] and will experience variations in climate during its lifetime. Moreover, it exhibits high levels of genetic heterozygosity [54,121–127]. Variability in trait expression will have been affected by genotype, phenotypic plasticity [16,128] and potentially differences in phenology and in the land-use and climatic history of the study sites. Furthermore, a different choice of species may have led to a very different set of results and conclusions: ‘functional’ traits are predicted to pattern more strongly with climate for fast-growing and short-lived species (Fig 1). Nevertheless, these equivocations do not alter the basic message of this study. ‘Mechanistic’ traits must be routinely included in climate-related studies.
A preliminary assessment of the ‘climatic’ PCA 3 axis in oleaster
Oleaster is a thermophilic species with limited resistance to both cold and extreme aridity . Moreover, aridity is generally regarded as the key climatic factor determining species composition in Mediterranean vegetation. The ‘climatic’ PCA axis 3 was correlated positively with MAT, MAP, MTCM and AI and negatively with altitude (Table 10A). Thus, high values of PCA axis 3 equated to high mean annual temperature, high minimum temperature of the coldest month, high mean annual precipitation, high aridity and low altitude. In terms of the traits that define PCA axis 3 (Table 9), these climatic extremes were associated with low stomatal density (DS–) low leaf water content (SLWC–), small leaves (LL–) and high leaf construction costs (SLA+). The trends for DS were similar to those recorded elsewhere in relation to climate [129,130]. Similarly, elongate leaves with a potentially thinner boundary layer [99,131,132] tended to be associated with harsher climates. PCA axis 3 may identify a water-use/succulence dimension. Moreover, site 13, excluded for its extremely high values for LT, LWC and SLWC (Table 3), may perhaps represent an extremely ‘succulent’ outlying population.
Succulence is an ecologically important functional mechanism defined as the ‘storage of utilizable water in living tissues in one or several plant parts in such a way as to allow the plant to be temporarily independent from external water supply but to retain at least some physiological activity’ . However, structural and physiological relationships involving succulence are complex [133–136]. As a result, whether PCA axis 3 identifies ‘succulence’, and provides a temporary drought avoidance mechanism, still requires experimental verification. Nevertheless, whatever the exact functional origins of climate-related PCA axis 3, its recognition was, importantly, only made possible through the inclusion of several traits not customarily included in trait-based ecological studies.
The way forward–an olive branch in the ‘functional’ versus ‘mechanistic’ debate
Our results, and most of the relationships included in our literature review, point to ‘mechanistic’ traits being diagnostically superior to ‘functional’ ones in climate studies. Nevertheless, we believe it counterproductive to focus entirely on this ‘mechanistic’ superiority. To re-iterate arguments from the Introduction, ‘mechanistic’ studies are time-consuming with small datasets produced and species chosen primarily for ecological relevance. Without a level of co-ordination not currently in place between related ‘mechanistic’ investigations, precision of measurement will be offset by few shared species and no integration of findings (i.e. little generality). Trait based ecology, and ‘functional’ traits, can potentially provide this missing generality by producing large ecologically-balanced datasets. However, as in this study, results may require mechanistic clarification. Importantly, as currently implemented, trait-based ecology is methodologically flawed. Specialization routinely occurs at the cellular/biochemical level but may additionally be identified at a higher organizational scale by measuring organs or whole plants. So far, few suitable methodologies are available for the large-scale measurement of traits that can only be identified at the lowest, most fundamental cellular/biochemical level. As a result, the size of plants and their parts, plus SLA and LDMC, which can be measured using whole leaves, stand imprecisely at the centre of meta-analyses in trait-based ecology [12,13]. In contrast, some important ecological specializations expressed primarily at the cellular/biochemical level (e.g. aluminium tolerance in acidic soils and restriction by climate [47,137]) remain outside the scope of these meta-analyses. Moreover, this study only partly redresses this ‘climatic imbalance’. Many addition simply-measured ‘mechanistic’ traits will be required to routinely add a comprehensive climatic dimension to trait-based studies.
Volaire  identified ‘functional’ traits as dealing with ecological strategies relating to multi-environmental factors and studied implicitly over long timescales. This is true but, equally, it is the product of methodological constraints rather than an ideological choice. Both the ‘mechanistic’ and ‘functional’ trait approaches have strengths, and weaknesses, but similar goals. In our search to understand and quantify impacts of changing climate on global vegetation composition and ecosystem function, the challenge will be to combine the strengths of both approaches–and to use both types of traits. ‘Mechanistic’ and ‘functional’ traits both contribute to our proposed plant-climate model (Fig 1) and each may be expected to add more generally to our understanding of climate-related processes.
S1 Table. Percentage coefficient of variation (CV) for leaf functional traits including minimum (CVmin) and maximum values CVmax).
S2 Table. Correlation matrix for CV values of traits (n = 18) with statistically significant relationships in bold.
We thank members of the International Associated Laboratory—EVOLEA and BioAgrodiversity team membres for helpful discussions and comments. We are very grateful to Abdelatif El Ouahrani and Mhammad Hossni for assistance during fieldwork, Emmanuel Paradis and Allowen Evin for the statistical advice. We thank the two anonymous reviewers for the constructive feedback on earlier version of the manuscript.
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