Damien Bonal
email: bonal@nancy.inra.fr

Benoît Burban

Clément Stahl
email: clement.stahl@ecofog.gf

Fabien Wagner
email: wagner.h.fabien@gmail.com

Bruno Hérault
email: bruno.herault@ecofog.gf

Jean-Michel Leban

Benoit Burban
email: benoit.burban@ecofog.gf

& Benoit Burban

The response of tropical rainforests to drought-lessons from recent research and future prospects

Keywords: Carbon, Climate, Drought, Global change, Growth, Mortality, Soil, Tropical, Water

de niveau recherche, publiés ou non, émanant des établissements d'enseignement et de recherche français ou étrangers, des laboratoires publics ou privés.

Introduction

Human-induced climate changes have begun to deeply impact boreal and temperate forest ecosystems (e.g. [START_REF] Ciais | Europe-wide reduction in primary productivity caused by the heat and drought in[END_REF]), but whether they are already affecting ecological functions in tropical rainforests is still an open question. Answering this question is one of the greatest challenges for scientists studying global change and for community or functional ecologists, since tropical ecosystems represent 34 % of gross primary terrestrial productivity [START_REF] Beer | Terrestrial gross carbon dioxide uptake: global distribution and covariation with climate[END_REF] and play a major role in carbon and water cycles at the global scale.

Tropical regions are characterized by high annual rainfall and high evapotranspiration. Nevertheless, a strong seasonality in precipitation and solar radiation levels (partly determined by cloud cover) occurs in most tropical regions around the world. These variations are partly driven by atmospheric movements related to the latitudinal changes in the intertropical conversion zone; they may lead to soil drought conditions. In environmental science, drought is defined as "a prolonged period of scanty rainfall". This definition describes a "climatic" point of view, related to the amount of precipitation reaching the ground. However, depending on soil type, soil drainage conditions, evapotranspiration levels and depth of soil water extraction by roots, a period of scanty rainfall may-or may not-severely reduce the amount of soil water available to plants, animals or microbes. In this context, the literature on the effect of drought on tropical rainforest ecosystems does not systematically and precisely define what is meant by "drought". Therefore, comparison of drought effects is not so obvious. Nevertheless, three types of drought are intensively studied in the current literature on tropical rainforests: seasonal droughts, extreme droughts and experimental droughts:

-Seasonal droughts correspond to seasonal variations in rainfall at a given site. This definition is based on longterm observations of precipitation regimes. One can expect that tropical rainforests are adapted to endure these seasonal droughts, as species have evolved under these conditions. Nevertheless, these seasonal variations influence ecosystem functioning and we thereafter review the existing knowledge on their response. -Extreme droughts correspond to a period of abnormally low rainfall. A number of extreme drought events hit the tropical regions around the world over the past decades. Some may be explained by El Niño-Southern Oscillation (ENSO) events (1982/1983, 1986/1987, 1997/1998) (in [START_REF] Marengo | The drought of 2010 in the context of historical droughts in the Amazon region[END_REF]: they have been associated with a rise in equatorial ocean surface temperatures and possibly also with modifications in the movement of the intertropical convergence zone [START_REF] Li | Rainfall and its seasonality over the Amazon in the 21st century as assessed by the coupled models for the IPCC AR4[END_REF]). However, in Amazonia, other major droughts are clearly unrelated to ENSO events (1980,2005,2010); they are linked to elevated surface temperatures in the Atlantic Ocean [START_REF] Marengo | Hydroclimatic and ecological behaviour of the drought of Amazonia in 2005[END_REF][START_REF] Marengo | The drought of 2010 in the context of historical droughts in the Amazon region[END_REF]. These extreme events may differ in intensity and duration and in the location and number of epicentres (see for instance the drought in 2005 vs. 2010 as illustrated in Fig. 1; [START_REF] Lewis | The 2010 Amazon Drought[END_REF]. They nevertheless strongly influence the functioning of tropical rainforests and even endanger them. Thereafter, we use the existing knowledge on their impact to emphasize the limits to which these ecosystems may adapt. -Experimental droughts correspond to through-fall exclusion experiments (Fig. 2). A given percentage of precipitation can be excluded from a given zone, and local consequences on soil, tree or ecosystem functioning are monitored. The major drawback of this approach is the surface of the considered zone: it is usually reduced (usually less than one or a few hectares). Several experiments have yet been conducted in wet tropical or subtropical regions. A list of these experiments with corresponding references is given in Table 1. As for extreme drought events, these experiments bring highly valuable information on the mechanisms involved in the response of these ecosystems to drought.

Considering these three types of drought and their specific effects on tropical forest ecosystems, we separate in this review the effects of recurrent seasonal drought on ecosystem functioning to the ones of extreme droughts and experimental ones (cf. list in Table 2). We thus focus on (i) what can be learnt from seasonal drying and (ii) what might be the consequences of more intense and/or more frequent droughts in the future. The latter question is a burning one as global earth models have made it possible to simulate an increase in the frequency and intensity of drought events in tropical regions (e.g. [START_REF] Cox | Amazonian forest dieback under climate-carbon cycle projections for the 21st century[END_REF][START_REF] Cox | Sensitivity of tropical carbon to climate change constrained by carbon dioxide variability[END_REF][START_REF] Poulter | Robust dynamics of Amazon dieback to climate change with perturbed ecosystem model parameters[END_REF]. The earliest simulations were highly criticized and [START_REF] Steinkamp | Is drought-induced forest dieback globally increasing?[END_REF], based on a global modelling analysis, concluded that there has not been any general drying trend or increase in extreme mortality events in tropical forests over the past decades. Yet, at least for the Amazonian region, global climate models converge to simulate a change in rainfall regime in this region and drier conditions over the twenty-first century [START_REF] Malhi | Exploring the likelihood and mechanism of a climate-change-induced dieback of the Amazon rainforest[END_REF]. Our ability to evaluate the impact of climatic change on the functioning of tropical rainforest ecosystems in the future will depend on observational, experimental and modelling approaches which include extreme drought conditions.

In this context, a considerable effort is being made worldwide to better understand the effect of drought on carbon and water cycles in tropical ecosystems at different spatial (forest stand to region) or temporal (seasonal to yearly) scales. Major research programmes have been and are being conducted in Central and South America, Asia and Africa. Within this framework, numerous new results have been published over the past 5 years. Hereafter, we provide a comprehensive review of these recent studies and discuss whether we are currently able to evaluate the response of tropical rainforests to the future climate conditions in these regions. We also synthetize the existing knowledge on the mechanisms leading to these effects. Considerable knowledge has been accumulated on the physiological attributes of tropical rainforest tree species and their ability to support drought events. A review of this present knowledge would be highly valuable, but to keep the scope of this article within acceptable limits, we concentrate on community-and ecosystem-level responses to drought, rather than on tree-or species-level responses. We include 172 papers in this review, among which 88 were published over the past 5 years (2010)(2011)(2012)(2013)(2014)(2015).

2 The influence of drought on tropical rainforest ecosystems

Tree mortality

As pointed out in Table 2, we were not able to find any information in the literature on the seasonal variations in mature tree mortality in tropical rainforest ecosystems. The main reason is that (i) tree mortality under non-exceptional years randomly occurs among seasons and (ii) seasonal droughtinduced mortality is hard to detect given that mortality is a punctual and rare phenomenon difficult to catch and model apart from exceptional events [START_REF] Hérault | Toward trait-based mortality models for tropical forests[END_REF]. This pattern is also consistent with the hypothesis that tropical rainforests are well-adapted to recurrent seasonal variations in soil water availability.

In contrast, the extreme drought that occurred in Amazonia in 2005 clearly resulted in abnormally high tree mortality rates [START_REF] Phillips | Drought sensitivity of the Amazon rainforest[END_REF][START_REF] Phillips | Drought-mortality relationships for tropical forests[END_REF]. Similar major die-off events were observed in Amazonia following an ENSO event [START_REF] Williamson | Amazonian tree mortality during the 1997 El Niño drought[END_REF], in Panama [START_REF] Condit | Mortality rates of 205 neotropical tree and shrub species and the impact of a severe drought[END_REF], in tropical rainforests in China (2009China ( -2010, 75 , 75 % increase in mortality rate; [START_REF] Tan | High sensitivity of a tropical rainforest to water variability: evidence from 10 years of inventory and eddy flux data[END_REF]) and in East Kalimantan on Borneo Island following an ENSO event (10-20 % increase in mortality rate; [START_REF] Slik | El Nino droughts and their effects on tree species composition and diversity in tropical rain forests[END_REF]. Furthermore, in two sites in Amazonia (Caxiuanã and Tapajós) on long-term monitoring plots with through-fall exclusion, tree mortality also strongly increased (100 %) a few years after the beginning of the experiment compared to controls [START_REF] Da Costa | Effect of 7 yr of experimental drought on vegetation dynamics and biomass storage of an eastern Amazonian rainforest[END_REF]. In contrast, no clear change in mortality rates was observed in Central Kalimantan, Indonesia, after the 1997 drought [START_REF] Nishimua | Mortality and growth of trees in peat-swamp and heath forests in central Kalimantan after severe drought[END_REF]). Increased mortality rates in extreme drought conditions as compared to recurrent seasonal droughts clearly point out to the limits that these ecosystems are able to support. These extreme drought events or experimental studies bring extremely valuable information to where these ecosystems can be pushed out by limited water conditions.

Comparing mortality rates after extreme drought events among sites distributed worldwide is perilous because climate conditions, species composition, soil conditions, history and drought severity differ. Nevertheless, [START_REF] Phillips | Drought-mortality relationships for tropical forests[END_REF] concluded that for comparable drought intensities, mortality rates in Asian tropical forests were stronger than in the Amazon. More intensive research programmes should be implemented so as to confirm such spatial trends and improve ecosystem and earth model simulations, particularly in poorly studied tropical rainforests like the ones in Africa and Asia: several What mechanisms might explain the higher mortality events following extreme droughts? This question does not apply solely to tropical forest ecosystems, and a large and recent literature for various ecosystems around the world suggests that both carbon starvation and hydraulic failure processes are involved (e.g. [START_REF] Hartmann | Research frontiers in drought-induced tree mortality: crossing scales and disciplines[END_REF]. The "carbon starvation hypothesis" was developed by [START_REF] Mcdowell | Mechanisms of plant survival and mortality during drought: Why do some plants survive while others succumb to drought?[END_REF] (see also the recent paper of [START_REF] Mcdowell | Evaluating theories of droughtinduced vegetation mortality using a multimodel-experiment framework[END_REF] and [START_REF] Sevanto | How do trees die? A test of the hydraulic failure and carbon starvation hypotheses[END_REF]) and states that tree mortality occurs mainly because reduced photosynthesis during drought periods limits the accumulation of non-structural carbohydrate compounds in trees. In contrast, hydraulic failure occurs when xylem vessels are embolized. Several studies on tropical rainforests have clearly shown strong limitation of water transported through the xylem during dry periods (e.g. [START_REF] Sobrado | Embolism vulnerability in drought-deciduous and evergreen species of a tropical dry forest[END_REF][START_REF] Lopez | Interspecific variation in xylem vulnerability to cavitation among tropical tree and shrub species[END_REF][START_REF] Fisher | Evidence from Amazonian forests is consistent with isohydric control of leaf water potential[END_REF][START_REF] Fisher | The response of an Eastern Amazonian rain forest to drought stress: results and modelling analyses from a throughfall exclusion experiment[END_REF], thus supporting the hydraulic failure hypothesis. In contrast, Metcalfe et al. (2010b) suggest that the higher mortality in through-fall exclusion stands could be explained by carbon starvation. It is now well-known that these processes represent synergistic responses to drought, but the main issue now is to understand how these processes are linked. Because the methodologies used to assess the mechanisms causing tree mortality are complex and highly time-consuming and rely on the occurrence of major droughts, we still lack enough data to decipher and understand the origin of tropical tree mortality. This limits our ability to simulate the future of these ecosystems.

It is also important to note that several studies have reported that the increase in mortality in both through-fall exclusion studies [START_REF] Da Costa | Effect of 7 yr of experimental drought on vegetation dynamics and biomass storage of an eastern Amazonian rainforest[END_REF]) and under natural conditions [START_REF] Phillips | Drought sensitivity of the Amazon rainforest[END_REF][START_REF] Phillips | Drought-mortality relationships for tropical forests[END_REF] was higher for large trees than for small ones. This pattern was observed in Amazonia and Borneo [START_REF] Phillips | Drought-mortality relationships for tropical forests[END_REF], but not in Asian forests [START_REF] Aiba | Effects of the 1997-98 El Nino drought on rain forests of Mount Kinabalu, Borneo[END_REF]Itoh et al. 2012a, b). Higher mortality for large trees may be related to higher evaporative demand (higher vapour pressure deficit at the top of the canopy) [START_REF] Saatchi | Persistent effects of a severe drought on Amazonian forest canopy[END_REF] or to a higher risk of hydraulic failure because of tree height. Some other studies also reported slightly higher mortality rates for trees with low density wood than for those with higher density wood [START_REF] Phillips | Drought-mortality relationships for tropical forests[END_REF][START_REF] Rossi | Identifying climatic drivers of tropical forest dynamics[END_REF]. Part of these differences could be linked to differences in hydraulic failure among trees, as wood density is linked to xylem structure.

It is also important to remember that extreme mortality events can also have positive feedbacks on ecosystem dynamics and functioning. Standing dead trees and/or large fallen trees modify the structure of the canopy, increase canopy openness and enhance radiation within the canopy and on the ground…, thus changing local environmental conditions [START_REF] Condit | Changes in tree species abundance in a Neotropical forest over eight years: impact of climate change[END_REF][START_REF] Holmgren | El Nino effects on the dynamics of terrestrial ecosystems[END_REF][START_REF] Slik | El Nino droughts and their effects on tree species composition and diversity in tropical rain forests[END_REF]). These conditions favour the establishment of fast growing trees and the growth of neighbouring trees, thus locally contributing to increased photosynthesis and ecosystem carbon uptake. Nevertheless, fast growing trees are characterized by low wood density and are likely to be more prone to embolism (e.g. [START_REF] Hacke | Trends in wood density and structure are linked to prevention of xylem implosion by negative pressure[END_REF]). In the mid to long term, these changes may thus negatively influence the carbon balance of these forests. Whether the recent demonstration by [START_REF] Brienen | Long-term decline of the Amazon carbon sink[END_REF] that the biomass dynamics of the Amazon rainforest over the past three decades show a long-term decreasing trend of carbon accumulation is consistent with this pattern is a worthy question.

Tree growth

Strong seasonal variations in tree growth (diameter increment) in tropical rainforests have been observed [START_REF] Tian | Effect of interannual climate variability on carbon storage in Amazonian ecosystems[END_REF][START_REF] Baker | Associations between tree growth, soil fertility and water availability at and regional scales in Ghanian tropical rain forest[END_REF][START_REF] Nepstad | Amazon drought and its implications for forest flammability and tree growth: a basin-wide analysis[END_REF][START_REF] Da Costa | Effect of 7 yr of experimental drought on vegetation dynamics and biomass storage of an eastern Amazonian rainforest[END_REF][START_REF] Stahl | Seasonal variation in atmospheric relative humidity contributes to explaining seasonal variation in trunk circumference of tropical rain forest trees in French Guiana[END_REF][START_REF] Grogan | The impact of annual and seasonal rainfall patterns on growth and phenology of emergent tree species in Southeastern Amazonia, Brazil[END_REF][START_REF] Wagner | Water availability is the main climate driver of neotropical tree growth[END_REF][START_REF] Wagner | Asynchronism in leaf and wood production in tropical forests: a study combining satellite and ground-based measurements[END_REF][START_REF] Wagner | Pan-Tropical analysis of climate effects on seasonal tree growth[END_REF]: a decrease in tree growth is usually observed during drought periods in inventory plots, followed by a strong increase at the onset of the rainy season.

Extreme droughts reduce tropical forest carbon storage by decreasing or even suppressing tree growth as compared to years with lower soil moisture deficits. [START_REF] Phillips | Drought sensitivity of the Amazon rainforest[END_REF] concluded that the 2005 extreme drought event in Amazonia halted the long-term increase in aboveground biomass (since the 1950s) in a significant number of study plots. It may be expected that water-stress-induced variation in tree growth response may be dependent to topographic position, as suggested by indirect observations [START_REF] Silva | Response of an oldgrowth tropical rainforest to transient high temperature and drought[END_REF]), but there is a lack of evidence on that point.

The causes for a decline in tree growth under drought conditions are multiple:

(i) Firstly, a methodological remark must be made. Growth measurements based on dendrometer bands installed around tree trunks must be used with caution, since the bands react to bark thickness and may shrink during dry periods (because of a drier atmospheric air, e.g. [START_REF] Stahl | Seasonal variation in atmospheric relative humidity contributes to explaining seasonal variation in trunk circumference of tropical rain forest trees in French Guiana[END_REF]. A decrease in trunk circumference during dry periods, or at least a decrease in circumference increment, could therefore be due to the shrinkage alone, or to a "real" decrease in tree growth (cell division in cambial tissues), or both. This widely used methodology has proven efficient to study long-term tree growth, but short-term variations (at seasonal scale) can lead to misinterpretation. Chitra-Tarak et al. ( 2015) have recently published a novel method to take this bias into account. (ii) Soil water has been found to be a predominant driver of seasonal variations in tree growth. Reduced relative extractable water during drought periods was found to be the main environmental factors causing temporal variations in tree growth in an extensive study on 205 trees in French Guiana [START_REF] Wagner | Modeling water availability for trees in tropical forests[END_REF]. Precipitation and the duration of the drought season were the best predictors of tree growth variations in an African study [START_REF] Ouédraogo | Slow-growing species cope best with drought: evidence from longterm measurements in a tropical semi-deciduous moist forest of Central Africa[END_REF]. This was also the case in an overview across tropical regions [START_REF] Wagner | Pan-Tropical analysis of climate effects on seasonal tree growth[END_REF]). (iii) Third, solar radiation and daily minimum air temperature also contribute to seasonal variations in tree growth, though to a lesser extent than soil water availability [START_REF] Clark | Annual wood production in a tropical rain forest in NE Costa Rica linked to climatic variation but not to increasing CO 2[END_REF][START_REF] Wagner | Water availability is the main climate driver of neotropical tree growth[END_REF]. The air temperature effect may be related to the limiting effect of high temperatures on photosynthesis. Interpreting the radiation effect is complex, as radiation may indeed influence photosynthesis levels. Yet, photosynthesis and growth are not directly linked: non-structural carbohydrates stored in trees also contribute to secondary growth, with various time lags (days to months) [START_REF] Richardson | Seasonal dynamics and age of stemwood nonstructural carbohydrates in temperate forest trees[END_REF].

The physiological mechanisms leading to seasonal variations in tree growth are not fully understood either. Secondary growth is known to decrease during drought periods when xylem embolism occurs, resulting in the disruption of water columns in the trunk and in branches and in the reduction of water supply to leaves [START_REF] Tyree | Summer and winter embolism in oakimpact on water relations[END_REF]. The role of non-structural carbohydrate reserves should be considered too: these reserves may not only play a major role in explaining seedling survival during drought periods [START_REF] Obrien | Drought survival of tropical tree seedlings enhanced by non-structural carbohydrate levels[END_REF]. They may also influence intra-annual variations in tree growth [START_REF] Würth | Non-structural carbohydrate pools in a tropical forest[END_REF][START_REF] Richardson | Seasonal dynamics and age of stemwood nonstructural carbohydrates in temperate forest trees[END_REF]. [START_REF] Doughty | Allocation trade-offs dominate the response of tropical forest growth to seasonal and interannual drought[END_REF] also emphasized the role of carbon allocation to the different tree compartments (leaf, fruit, branch and root) to explain seasonal variations in tree growth in Bolivian tropical rainforests. These authors even concluded that seasonal shifts in allocation (particularly the trade-off between above-and belowground compartments) rather than changes in productivity explain seasonal changes in tree growth.

Interestingly, drought does not influence growth in trees of different sizes or with differing growth rates in a similar way: long-term drought in through-fall exclusion experiments mainly affected the growth of large trees, whereas the small trees were barely impacted (da Costa et al. 2010). Similar trends were observed in natural forests in Amazonia and Africa [START_REF] Ouédraogo | Slow-growing species cope best with drought: evidence from longterm measurements in a tropical semi-deciduous moist forest of Central Africa[END_REF][START_REF] Phillips | Drought sensitivity of the Amazon rainforest[END_REF][START_REF] Wagner | Asynchronism in leaf and wood production in tropical forests: a study combining satellite and ground-based measurements[END_REF][START_REF] Wagner | Pan-Tropical analysis of climate effects on seasonal tree growth[END_REF]. Furthermore, trees with high radial growth rates under moist conditions showed the strongest relative decrease under through-fall conditions in Indonesia [START_REF] Moser | Replicated throughfall exclusion experiment in an Indonesian perhumid rainforest: wood production, litter fall and fine root growth under simulated drought[END_REF]). These effects are not intuitive since reduced soil water availability necessarily displays a vertical gradient: the top layers are usually drier than the deeper ones. One could therefore expect that trees with superficial roots would be affected the most. Yet, Stahl et al. (2013b) demonstrated that there is no clear relationship between tree size and soil water extraction depth during the dry season: small trees are also able to use water from deep soil layers. Other explanations may have to do with ontogenetic shifts in drought-adaptive capacities [START_REF] Cavender-Bares | Changes in drought response strategies with ontogeny in Quercus rubra: implications for scaling from seedlings to mature trees[END_REF] or in hydraulic failure/ carbon allocation strategies.

Carbon fluxes

An important consequence of higher mortality rates during broad-scale mortality events is the reduced capacity of impacted forests to absorb CO 2 and the huge amounts of carbon that can be released into the atmosphere as the dead trees decomposed. This decomposition is slow (one to several decades) and varies widely according to wood density and branch or trunk size [START_REF] Hérault | Modeling decay rates of dead wood in a neotropical forest[END_REF]. Direct, long-term measurements of carbon fluxes are recorded at various eddy flux tower sites in tropical rainforest ecosystems (now in Amazonia, Africa and Asia) and allow to characterize seasonal variations in carbon fluxes (Fig. 3). Gross primary productivity (GPP) and ecosystem respiration (ER)-the two CO 2 fluxes that characterize the main exchange in carbon between the ecosystem and the atmosphere-usually decrease during seasonal droughts (see van One major result obtained thanks to these studies is that differential changes in ecosystem photosynthesis (GPP) and respiration (ER) during dry periods induce large seasonal variations in the ecosystem carbon balance, as determined by net ecosystem carbon exchange (NEE). NEE is calculated as the algebraic difference between ER and GPP [the ecosystem is considered to be a carbon sink when NEE is negative]. Large discrepancies in seasonal variations in NEE across tropical rainforests have been found. Some studies showed no clear effect of seasonal soil drought on NEE [START_REF] Carswell | Seasonality in CO 2 and H 2 O flux at an eastern Amazonian rain forest[END_REF]). In contrast, other studies showed a decrease in carbon uptake during dry periods [START_REF] Williams | Seasonal variation in net carbon exchange and evapotranspiration in a Brazilian rain forest: a modelling analysis[END_REF][START_REF] Keller | Ecological research in the large-scale biosphere-atmosphere experiment in Amazonia: early results[END_REF]), whereas others showed higher [more negative] NEE values during dry seasons than during wet seasons [START_REF] Saleska | Carbon in amazon forests: unexpected seasonal fluxes and disturbance-induced losses[END_REF][START_REF] Goulden | Diel and seasonal patterns of tropical forest CO 2 exchange[END_REF][START_REF] Baker | Seasonal drought stress in the Amazon: reconciling models and observations[END_REF][START_REF] Bonal | The impact of severe dry season on net ecosystem exchange in the Neotropical rainforest of French Guiana[END_REF][START_REF] Yan | Seasonal and inter-annual variations in net ecosystem exchange of two old-growth forests in southern China[END_REF]. At the latter sites, tropical rainforest ecosystems accumulate more carbon when water is a limiting factor than during the wet seasons. Some of these discrepancies could be related to the overestimation of ER in early studies that used the eddy covariance method (see [START_REF] Saleska | Carbon in amazon forests: unexpected seasonal fluxes and disturbance-induced losses[END_REF][START_REF] Kruijt | The robustness of eddy correlation fluxes for Amazon rain forest conditions[END_REF]). They also arise because of differences in species composition, soil conditions and partly also to drought stress levels reached at the sites.

Under extreme drought conditions, GPP is generally moderately further impacted by these extreme conditions, while the decrease in ER is usually much stronger than under recurrent seasonal droughts (synthetized in [START_REF] Shi | Differential effects of extreme drought on production and respiration: synthesis and modeling analysis[END_REF]. This suggests that drought severity could be driving the relative decrease in GPP and ER in these ecosystems. If this is verified, such patterns should be included in modelling approaches. A question which merits further attention then arises: what is the future of the carbon that is not released during severe dry periods, as compared to moderate dry ones? Is this carbon directly released to the atmosphere once heavy rainfalls occur or is it, partly or completely, stored in the ground?

The following mechanisms have been identified as contributing to the GPP and ER pattern under seasonal or extreme droughts:

(i) Tree root access to deep soil layers [START_REF] Nepstad | The role of deep roots in the hydrological and carbon cycles of Amazonian forests and pastures[END_REF][START_REF] Markewitz | Soil moisture depletion under simulated drought in the Amazon: impacts on deep root uptake[END_REF]Stahl et al. 2013b) limits the negative effect of reduced rainfall on photosynthetic activity. Indeed, though the root biomass of tropical rainforest trees is concentrated in the upper soil layers [START_REF] Nepstad | The role of deep roots in the hydrological and carbon cycles of Amazonian forests and pastures[END_REF], deep roots still play a crucial role in the water and carbon cycles in these ecosystems [START_REF] Nepstad | The role of deep roots in the hydrological and carbon cycles of Amazonian forests and pastures[END_REF]Stahl et al. 2013b). When soil water becomes limited in the upper soil layers, deep roots may provide water to the trees and thus help to prevent, or at least delay, the down-regulation of carbon and water fluxes.

Reduced rainfall conditions over several weeks or even months do not always result in an instantaneous lack of water for deep-rooted trees; delayed drought effects may be observed. The GPP of deep-rooted trees may therefore remain high during drought events. (ii) An increase in GPP could be expected during dry periods because of the production of new leaves [START_REF] Restrepo-Coupe | What drives the seasonality of photosynthesis across the Amazon basin? A cross-site analysis of eddy flux tower measurements from the Brasil flux network[END_REF]) and increased radiation [reduced cloud cover] as compared to wet periods [START_REF] Huete | Amazon rainforests greenup with sunlight in dry season[END_REF][START_REF] Brando | Seasonal and interannual variability of climate and vegetation indices across the Amazon[END_REF][START_REF] Samanta | Seasonal changes in leaf area of Amazon forests from leaf flushing and abscission[END_REF]). The negative effect of reduced solar radiation on tree photosynthesis and growth during the wet season was experimentally demonstrated by [START_REF] Graham | Cloud cover limits net CO 2 uptake and growth of a rainforest tree during tropical rainy seasons[END_REF]. This argument was also used by [START_REF] Condit | Tropical forest dynamics across a rainfall gradient and the impact of an El Nino dry season[END_REF] to explain high tree growth rates during the 1997-1998 ENSO event. However, this potential increase may be counterbalanced to some extent by the negative effect of drought on photosynthesis for the shallow-rooted trees when the dry season is moderate, or for most trees if the decrease in soil water availability is severe. The opposite trend between these different effects explains the complexity of the seasonal variations in GPP. (iii) ER is the sum of the CO 2 efflux from all the ecosystem compartments. One can expect a physiologically driven decrease in cell respiration under drought (see Atkin and Macherel 2009 for a review), but contrasting results have been published for tropical rainforest trees. A decrease in the CO 2 efflux from the leaves, trunks and coarse woody debris was found in several studies [START_REF] Chambers | Decomposition and carbon cycling of dead trees in tropical forests of the central Amazon[END_REF][START_REF] Chambers | Respiration from coarse wood litter in central Amazon forests[END_REF][START_REF] Nepstad | The effects of partial throughfall exclusion on canopy processes, aboveground production, and biogeochemistry of an Amazon forest[END_REF][START_REF] Stahl | Seasonal variations in stem CO 2 efflux in the Neotropical rainforest of French Guiana[END_REF]Stahl et al. , 2013a;;[START_REF] Rowland | The response of tropical rainforest dead wood respiration to seasonal drought[END_REF][START_REF] Rowland | Evidence for strong seasonality in the carbon storage and carbon use efficiency of an Amazonian forest[END_REF]. However, others showed slightly higher autotrophic (root and leaf) CO 2 fluxes under dry conditions (Metcalfe et al. 2010a, b;[START_REF] Da Costa | Ecosystem respiration and net primary productivity after 8-10 years of experimental through-fall reduction in an eastern Amazon forest[END_REF]. Similarly, contrasting changes in soil CO 2 efflux have been found: a decrease in total soil respiration was observed in numerous studies (Araujo et al. 2002;[START_REF] Goulden | Diel and seasonal patterns of tropical forest CO 2 exchange[END_REF][START_REF] Hutyra | Seasonal controls on the exchange of carbon and water in an Amazonian rain forest[END_REF][START_REF] Bonal | The impact of severe dry season on net ecosystem exchange in the Neotropical rainforest of French Guiana[END_REF]). However, though some through-fall exclusion manipulation experiments confirmed this decrease [START_REF] Sotta | Effects of an induced drought on soil carbon dioxide (CO 2 ) efflux and soil CO 2 production in an Eastern Amazonian rainforest, Brazil[END_REF][START_REF] Van Straaten | Simulated drought reduces soil CO 2 efflux and production in a tropical forest in Sulawesi, Indonesia[END_REF][START_REF] Wood | Strong spatial variability in trace gas dynamics following experimental drought in a humid tropical forest[END_REF], other studies showed no effect of water exclusion on heterotrophic soil respiration [START_REF] Davidson | Effects of an experimental drought and recovery on soil emissions of carbon dioxide, methane, nitrous oxide, and nitric oxide in a moist tropical forest[END_REF]) and one even found an increase (total soil respiration; [START_REF] Cleveland | Experimental drought in a tropical rain forest increases soil carbon dioxide losses to the atmosphere[END_REF]. These discrepancies could be related to differences in soil type and potential local ecosystem and carbon cycling adaptations to climatic conditions [START_REF] Cleveland | Experimental drought in a tropical rain forest increases soil carbon dioxide losses to the atmosphere[END_REF]). However, the levels of drought stress reached at the study sites (seasonal vs. extreme) and the duration of the drought do not seem to contribute to explain these differences. These results underline the complexity of the carbon cycle in tropical ecosystems submitted to drought and make it difficult to simulate these response patterns with ecosystem or earth models.

Transpiration

Tropical rainforests play a major role in the global climate system because they exchange huge amounts of water and energy with the atmosphere. Droughts of varying intensity modify the hydrological cycle over these ecosystems [START_REF] Gloor | Intensification of the Amazon hydrological cycle over the last two decades[END_REF]. When tropical rainforests suffer from seasonal drought, a decrease in tree-and ecosystem-level evapotranspiration is observed [START_REF] Bonal | Late stage canopy tree species with extremely low δ 13 C and high stomatal sensitivity to seasonal soil drought in the tropical rainforest of French Guiana[END_REF]Stahl et al. 2013a).

When the drought conditions become harsher, the decrease in tree transpiration is much stronger, and [START_REF] Fisher | The response of an Eastern Amazonian rain forest to drought stress: results and modelling analyses from a throughfall exclusion experiment[END_REF] concluded that tree water use was restricted to 20 % of that in the control plots in a through-fall exclusion experiment. However, it is important to keep in mind that a decrease in evapotranspiration during a drought period actually reflects the combination of two opposite effects. First, high solar radiation during dry periods induces high evaporative demand [drier and warmer atmospheric air] that should theoretically lead to higher evapotranspiration rates. As an example, Fisher et al. ( 2007) confirmed higher transpiration during the dry season than during the wet season in Brazil. Second, a decrease in soil water availability leads to the down-regulation of stomatal conductance and thus to lower tree transpiration [START_REF] Bonal | Late stage canopy tree species with extremely low δ 13 C and high stomatal sensitivity to seasonal soil drought in the tropical rainforest of French Guiana[END_REF]Stahl et al. 2013a). This generally observed decrease in transpiration during droughts suggests a predominant down-regulation of transpiration (reduction in soil-toroot conductance and water transport) when soil water availability is strongly limited. Nevertheless, the effect of soil water drying and strong evaporative demand on stomatal regulation can be diverging [START_REF] Tardieu | Variability among species of stomatal control under fluctuating soil water status and evaporative demand: modelling isohydric and anisohydric behaviors[END_REF][START_REF] Tardieu | Control of leaf growth by abscisic acid: hydraulic or non-hydraulic processes?[END_REF]. The complexity of these effects should not be overlooked when investigating observed patterns, particularly in modelling analyses.

3 What faces tropical rainforests in the future?

Species composition

Based on biogeographical, taxonomic or molecular biology studies, it has now been widely accepted that the tree species composition in tropical rainforests evolved during the Late Pleistocene and Holocene periods in conjunction with the occurrence of drier and cooler periods [START_REF] Mayle | Millennial-scale dynamics of southern Amazonian rain forests[END_REF]. Even though major parts of tropical rainforests may have been remarkably resilient to dry climatic conditions [START_REF] Mayle | Impact of a drier Early-Mid-Holocene climate upon Amazonian forests[END_REF], the current species composition of these forests is directly linked to past climate changes [START_REF] Liu | Forest changes in the Amazon Basin during the last glacial maximum[END_REF]. Just as the tropical rainforest communities of today were shaped by past climate changes, so will tropical species distribution, community composition and diversity be altered if climate conditions drastically change in the near future [START_REF] Slik | El Nino droughts and their effects on tree species composition and diversity in tropical rain forests[END_REF][START_REF] Engelbrecht | Drought sensitivity shapes species distribution patterns in tropical forests[END_REF][START_REF] Da Costa | Effect of 7 yr of experimental drought on vegetation dynamics and biomass storage of an eastern Amazonian rainforest[END_REF]. [START_REF] Malhi | Exploring the likelihood and mechanism of a climate-change-induced dieback of the Amazon rainforest[END_REF] simulated that future climate conditions over Amazonia will be favourable for seasonal forests rather than for dry tropical forest or dry savannahs. In contrast, some global vegetation models predict a dramatic shift of the biome in Amazonia towards dry forests or even woodland savannahs [START_REF] Cox | Amazonian forest dieback under climate-carbon cycle projections for the 21st century[END_REF][START_REF] Chave | Floristic shifts versus critical transitions in Amazonian forest systems[END_REF]). These predictions are somehow catastrophic considering the known resilience of these ecosystems to drought events during the Holocene [START_REF] Mayle | Impact of a drier Early-Mid-Holocene climate upon Amazonian forests[END_REF]. Nevertheless, they are supported by a few observations in tropical rainforests where local species composition and community functioning appear to shift over two to three decades towards more xeric types, if soil water conditions are frequently limited (e.g. [START_REF] Condit | Ecological implications of changes in drought patterns: shifts in forest composition in Panama[END_REF][START_REF] Enquist | Long-term change within a Neotropical forest: assessing differential functional and floristic responses to disturbance and drought[END_REF]). This shift is associated with the contrasting vulnerability of tropical species to drought: for certain taxa, or size classes, or growth characteristics (fast vs. slow growing), or successional status (early vs. late stage), some species are subject to disproportionate mortality. Through-fall exclusion experiments have also revealed a strong variability among tree species, or tree genii, in their mortality rates [START_REF] Da Costa | Effect of 7 yr of experimental drought on vegetation dynamics and biomass storage of an eastern Amazonian rainforest[END_REF][START_REF] Nepstad | Mortality of large trees and lianas following experimental drought in an Amazon forest[END_REF]. A precise description of the functional characteristics of tropical tree species and their physiological and morphological response to drought is far from being complete. Nevertheless, important screenings of traits related to drought have been conducted over the past decades (e.g. [START_REF] Bonal | Late stage canopy tree species with extremely low δ 13 C and high stomatal sensitivity to seasonal soil drought in the tropical rainforest of French Guiana[END_REF][START_REF] Engelbrecht | Survival and ecophysiology of tree seedlings during El Nino drought in a tropical moist forest in Panama[END_REF][START_REF] Engelbrecht | Drought sensitivity shapes species distribution patterns in tropical forests[END_REF][START_REF] Engelbrecht | Comparative drought-resistance of seedlings of 28 species of co-occurring tropical woody plants[END_REF][START_REF] Bartlett | The determinants of leaf turgor loss point and prediction of drought tolerance of species and biomes: a global meta-analysis[END_REF][START_REF] Fortunel | Wood specific gravity and anatomy of branches and roots in 113 Amazonian rainforest tree species across environmental gradients[END_REF]. The vulnerability of tropical tree species to prolonged droughts diverges and is related to intrinsic differences in various leaf (e.g. turgor loss point, osmotic potential, stomatal closure, leaf thickness, specific leaf area, water use efficiency) and wood biological properties (e.g. xylem vessel size, wood specific gravity). Further comprehensive studies on the functional characteristics of tree species in Amazonia, Africa and Asia are still required.

As an example of shift in species composition, an increase in lianas, both in terms of individuals and biomass, has been documented over the past decade in tropical rainforests (see Schnitzer and Bongers 2011 for an overview). This change in distribution may have various origins (increasing forest disturbance, changes in land use, forest fragmentation…), but it has also been suggested that climate changes, along with extreme drought events, could be playing a major role. This remains to be proven; observations are recent and correlative changes are under study. Nevertheless, lianas are known to benefit, to the detriment of tree species, from drier air (increased evaporative demand) or soils (decreased soil water availability) [START_REF] Schnitzer | A mechanistic explanation for global patterns of liana abundance and distribution[END_REF][START_REF] Schnitzer | Increasing liana abundance and biomass in tropical forests: emerging patterns and putative mechanisms[END_REF]. Climatic conditions in the future may continue to be favourable to lianas and allow them to colonize new tropical rainforests, or at least to accentuate their contribution to ecosystem biomass and productivity.

These functional considerations should not hide one very important aspect in community ecology: tropical rainforests are the most diverse forests in the world (at least in terms of tree species). For a large range of ecosystem services, more diverse forest ecosystems perform better that pure ones because of positive interactions among tree species for resource acquisition (facilitation or niche differentiation mechanisms; see [START_REF] Cardinale | Biodiversity loss and its impact on humanity[END_REF] for a review). Basic theoretical ecology also suggests that biodiversity insures ecosystems against alteration of ecosystem functions, the insurance hypothesis [START_REF] Yachi | Biodiversity and ecosystem productivity in a fluctuating environment: the insurance hypothesis[END_REF]. Numerous species with a broad range of functional characteristics provide greater ecological overlaps so that if some species are loss, the remaining ones maintain similar levels of ecosystem functioning. In contrast, [START_REF] Mouillot | Rare species support vulnerable functions in high-diversity ecosystems[END_REF] recently demonstrated the major role of rare species and functional vulnerability in the stability of ecosystem functioning. Unfortunately, very few studies on the relationship between biodiversity and ecosystem functioning have been conducted in tropical regions and those few mainly concern experimental plantations (e.g. [START_REF] Potvin | Biodiversity enhances individual performance but does not affect survivorship in tropical trees[END_REF][START_REF] Forrester | The spatial and temporal dynamics of species interactions in mixed-species forests: from pattern to process[END_REF]. Tropical rainforests with different levels of species diversity or with different species composition may respond differently to future droughts. A completely new area in ecological research is needed to answer this question.

Phenology patterns

Tropical rainforests are composed of species that cover the full range of leaf phenology patterns (i.e. emergence and fall), from strict deciduousness to evergreen [START_REF] Loubry | Déterminismes du comportement phénologique des arbres en forêt tropicale humide de Guyane Française[END_REF][START_REF] Viennois | Multiresolution quantification of deciduousness in West-Central African forests[END_REF]. The leaf area index (LAI) in these ecosystems remains high all year long and they are therefore classified as evergreen forests. Nevertheless, inconsistent seasonal patterns in LAI have been observed in Amazonia. [START_REF] Malhado | Seasonal leaf dynamics in an Amazonian tropical forest[END_REF] and [START_REF] Wagner | Asynchronism in leaf and wood production in tropical forests: a study combining satellite and ground-based measurements[END_REF] observe no seasonal change in LAI, whereas several studies conclude to clear seasonal dynamics in LAI or litterfall (e.g. [START_REF] Juarez | An improved estimate of leaf area index based on the histogram analysis of hemispherical photographs[END_REF]. A peak in litterfall is usually observed during the early stages of the dry season in Amazonia (see [START_REF] Chave | Regional and temporal patterns of litterfall in tropical South America[END_REF] for an overview). The origin of this later pattern remains unexplained: reduced water availability does not seem to provide an explanation [START_REF] Wright | Seasonal drought and leaf fall in a tropical forest[END_REF][START_REF] Xiao | Detecting leaf phenology of seasonally moist tropical forests in South America with multi-temporal MODIS images[END_REF][START_REF] Miranda | Leaf phenology and water potential of five arboreal species in gallery and montane forests in the Chapada Diamantina, Bahia; Brazil[END_REF]. Seasonal variations in leaf phenology were found to be driven by solar irradiance [START_REF] Wright | Light and the phenology of tropical trees[END_REF][START_REF] Xiao | Detecting leaf phenology of seasonally moist tropical forests in South America with multi-temporal MODIS images[END_REF][START_REF] Wagner | Asynchronism in leaf and wood production in tropical forests: a study combining satellite and ground-based measurements[END_REF]. The peak in leaf fall coincides with a peak in radiation [START_REF] Wagner | Asynchronism in leaf and wood production in tropical forests: a study combining satellite and ground-based measurements[END_REF]) and is associated with a greater emergence of new leaves at the onset and during the dry season, a period when cloud cover is usually low or absent and solar radiation is therefore strong. [START_REF] Kim | Seasonal carbon dynamics and water fluxes in an Amazon rainforest[END_REF] showed that including a light-controlled phenology module into a terrestrial biosphere model (ED2 model) strongly improved its ability to capture seasonal patterns in net ecosystem productivity and litterfall fluxes. The greater proportion of young leaves during the dry season could enhance carbon assimilation during the dry season and at the onset of the wet season, at least as long as stomatal regulation related to drought stress does not limit photosynthesis. Indeed, young leaves are characterized by higher photosynthetic capacity than mature or senescent ones. However, this argument has been contradicted by studies showing a delayed development of the photosynthetic apparatus in young tropical rainforest leaves and lower photosynthetic efficiency compared to mature ones [START_REF] Kursar | Delayed development of the photosynthetic apparatus in tropical rainforest species[END_REF].

When considering the influence of extreme drought events, strong changes in ecosystem leaf area were indeed observed [START_REF] Hilker | Vegetation dynamics and rainfall sensitivity of the Amazon[END_REF]). However, interestingly, long-term through-fall experiments showed no clear impact of severe drought on litterfall over the first and second year [START_REF] Brando | Drought effects on litterfall, wood production and belowground carbon cycling in an Amazon forest: results of a throughfall reduction experiment[END_REF]); a slight decline in litterfall compared to control plots occurred only at the third year. This pattern confirms the drought resistance of tropical ecosystems when an extreme event does not last too long, but also the limits to this resistance.

Optical remote sensing has been widely used over the past decade to analyse the effect of extreme drought on ecosystem phenology at various time scales and over large areas. After the discovery-using satellite measurements-of an unexpected canopy green-up during the dry season in Amazonia during the 2000-2005 period [START_REF] Huete | Amazon rainforests greenup with sunlight in dry season[END_REF]), Saleska et al. (2007) detected an increase of this green-up during the extreme dry season in 2005. This green-up was interpreted as being consistent with the leaf flush usually observed during dry conditions. However, Samanta et al. ( 2010)-and more recently [START_REF] Morton | Amazon forests maintain consistent canopy structure and greenness during the dry season[END_REF]-argued that these conclusions were based on irreproducible data and potential artefacts: the satellite data quality [partly due to cloud cover] may not have been good enough to support such a strong interpretation. The authors then concluded that no increase in green-up actually occurred during extreme drought events, a result consistent with the decline in greenness (less photosynthesis) during the 2010 drought event over Amazonia [START_REF] Xu | Widespread decline in greenness of Amazonian vegetation due to the 2010 drought[END_REF]). However, an increase in greenness was recently observed by [START_REF] Maeda | Can MODIS EVI monitor ecosystem productivity in the Amazon rainforest?[END_REF] during the dry season, even after correcting for all potential sun/sensor geometry artefacts. These results are clearly contradictory and a recent study tempted to reconcile these diverging views [START_REF] Hilker | Vegetation dynamics and rainfall sensitivity of the Amazon[END_REF]. These authors conclude that the new, better quality satellite data such as those obtained with C5-MODIS eliminate such potential artefacts and that the occurrence of canopy cover green-up during seasonal dry periods, or extreme ones, depends on whether trees can access to deep soil water. As a result, some parts of the Amazon forest do show green-up during the dry season, though limited, since, during the cloudy wet season, the reduced light limits ecosystem photosynthesis. However, in other parts of the Amazon forest where tree access to soil water is severely limited, no greening-up occurs; a decline in greenness may even be observed via satellite. Studying tropical forest phenology with satellites data is thus feasible, but precisely assessing the impact of severe drought events is not yet fully solved [START_REF] Hilker | Vegetation dynamics and rainfall sensitivity of the Amazon[END_REF].

Carbon balance

Considerable literature over the past decade has demonstrated the positive role of tropical rainforests in capturing large amounts of atmospheric CO 2 (e.g. [START_REF] Baker | Increasing biomass in Amazon forests[END_REF][START_REF] Malhi | The above-ground coarse wood productivity of 104 Neotropical forest plots[END_REF][START_REF] Ichii | Modeling the interannual variability and trends in gross and net primary productivity of tropical forests from 1982 to 1999[END_REF][START_REF] Lewis | Increasing carbon storage in intact African tropical forests[END_REF][START_REF] Phillips | Drought sensitivity of the Amazon rainforest[END_REF][START_REF] Pan | A large and persistent carbon sink in the world's forests[END_REF]. Net aboveground biomass gain has been confirmed on numerous inventory plots in Amazonia or Africa: [START_REF] Phillips | Recent changes in tropical forest biomass and dynamics[END_REF] estimate that the relative rate of increase is around 0.30 and 0.29 % for Amazonia and Africa, respectively. Accumulation of carbon in the tropical terrestrial biosphere strongly contributes to slowing the rate of increase of CO 2 into the atmosphere, thus reducing the greenhouse gas effect. Undisturbed tropical rainforests have been acting as a strong carbon sink in this way for decades.

The question now is whether they will be able to continue playing this role under future climate, particularly if the occurrence of extreme drought events increases. The large mortality event associated with the extreme 2005 drought in Amazonia was equivalent to several decades-worth of carbon accumulated by the tropical rainforest [START_REF] Phillips | Drought sensitivity of the Amazon rainforest[END_REF][START_REF] Gloor | The carbon balance of South America: a review of the status, decadal trends and main determinants[END_REF]. A recent analysis of atmospheric CO 2 measurements concluded that the unburned part of the Amazon basin [carbon release through fires is deducted in carbon balance calculations] shifted from a net carbon sink during a wet year to a carbon-neutral status during an extreme drought year (i.e. 2010) [START_REF] Gatti | Drought sensitivity of Amazonian carbon balance revealed by atmospheric measurements[END_REF]. This shift was explained not only by changes in air temperature and vapour pressure deficit, but also by reduced soil water availability. An increase in the frequency of such major drought events in the future is therefore likely to modify the positive carbon uptake role played by undisturbed tropical rainforests and may negate the positive fertilization effect of increased CO 2 concentrations [START_REF] Cox | Sensitivity of tropical carbon to climate change constrained by carbon dioxide variability[END_REF]). Yet, serious inconsistencies among simulation studies can be found: [START_REF] Phillips | Recent changes in tropical forest biomass and dynamics[END_REF] reviewed the predictions concerning the carbon balance in Amazonian and African tropical rainforest ecosystems: in the future, these ecosystems may act as potential sinks, or become carbon sources, or have a neutral balance.

Furthermore, a recent pan-tropical study based on 150 years of tree ring analysis showed that increased atmospheric CO 2 concentration induced an increase in intrinsic water use efficiency (the ratio of leaf CO 2 assimilation over stomatal conductance) but not an increase in individual tree growth [START_REF] Van Der Sleen | No growth stimulation of tropical trees by 150 years of CO 2 fertilization but water-use efficiency increased[END_REF].

The uncertainties around these simulations are largely related both to the structure and the parameterization of the global circulation vegetation models in use today. As for phenology patterns, a major challenge for remote sensing or modelling approaches is to reconcile satellite observations with observed measurements of ecosystem carbon fluxes and storage. A wide range of ecosystem or earth models have been elaborated and tested to date (e.g. [START_REF] Saleska | Carbon in amazon forests: unexpected seasonal fluxes and disturbance-induced losses[END_REF][START_REF] Ichii | Constraining rooting depths in tropical rainforests using satellite data and ecosystem modeling for accurate simulation of gross primary production seasonality[END_REF][START_REF] Baker | Seasonal drought stress in the Amazon: reconciling models and observations[END_REF][START_REF] Sitch | Evaluation of the terrestrial carbon cycle, future plant geography and climate-carbon cycle feedbacks using five Dynamic Global Vegetation Models (DGVMs)[END_REF][START_REF] Fisher | Assessing uncertainties in a second-generation dynamic vegetation model caused by ecological scale limitations[END_REF][START_REF] Sakaguchi | Natural and drought scenarios in an east central Amazon forest: fidelity of the Community Land Model 3.5 with three biogeochemical models[END_REF][START_REF] Rowland | Evidence for strong seasonality in the carbon storage and carbon use efficiency of an Amazonian forest[END_REF]) and a large body of literature addresses these issues. Though we will not discuss this literature in detail here, it is evident that no model is yet able to encompass all the complex plant-and ecosystem-water interactions under limiting soil water conditions. Solid improvements have been made over the past decade in matching the more mechanistic models with local observed data. [START_REF] Powell | Confronting model predictions of carbon fluxes with measurements of Amazon forests subjected to experimental drought[END_REF] perfectly summarizes the current state-of-the-art: "… terrestrial biosphere models are competent at predicting plant and ecosystem carbon fluxes under the present climate, but still require substantial development for predicting the consequences of severe drought scenarios.".

The influence of drought on the exchange of greenhouse gases other than CO 2 between tropical rainforests and the atmosphere is rather unknown. A few studies conducted over the past decade showed significant seasonal variations in N 2 O or CH 4 fluxes [START_REF] Davidson | Effects of an experimental drought and recovery on soil emissions of carbon dioxide, methane, nitrous oxide, and nitric oxide in a moist tropical forest[END_REF]Itoh et al. 2012a, b;[START_REF] Wood | Strong spatial variability in trace gas dynamics following experimental drought in a humid tropical forest[END_REF][START_REF] Yan | Responses of CO 2 , N 2 O and CH 4 fluxes between atmosphere and forest soil to changes in multiple environmental conditions[END_REF]), but further comprehensive studies are required in order to include the effect of drought on these fluxes in ecosystem or earth models.

Fires

A major risk of future droughts-and one that may radically change species composition-is forest fire. Natural forest fires occasionally occurred in tropical rainforests throughout the Holocene period [START_REF] Saldarriaga | Holocene fires in the northern Amazon basin[END_REF]) and contributed to shape the biogeography of the actual tropical rainforests.

Nevertheless, the major drought events of the past decades have resulted in an increased number of major forest fires in tropical rainforests [START_REF] Cochrane | Positive feedbacks in the fire dynamic of closed canopy tropical forests[END_REF][START_REF] Alencar | Forest understory fire in the Brazilian Amazon in ENSO and non-ENSO years: area burned and committed carbon emissions[END_REF][START_REF] Aragão | Interactions between rainfall, deforestation and fires during recent years in the Brazilian Amazonia[END_REF]). The risk of major fires is also expected to increase in the twenty-first century [START_REF] Davidson | The Amazon basin in transition[END_REF]). These fires have altered species composition and forest dynamics in large areas and will have long-term consequences on these ecosystems [START_REF] Brando | Abrupt increases in Amazonian tree mortality due to drought-fire interactions[END_REF]. Some evidence suggests that in tropical rainforests, selective logging [START_REF] Siegert | Increased damage from fires in logged forests during droughts caused by El Niño[END_REF], pasture burning [START_REF] Nepstad | Large-scale impoverishment of Amazonian forests by logging and fire[END_REF]) and forest fragmentation [START_REF] Cochrane | Climate change, human land use and future fires in the Amazon[END_REF] lead to an increased susceptibility of the forest canopy to fire. This increase is due to a greater amount of dead wood in these forests, a lower relative humidity in the understory which increases the drying speed of the dead wood and a greater penetration of forests by human activities. For example, opening of the canopy by logging generates faster air movements in the canopy so that the increase in fire-line intensity in logged forests in the Amazon region is estimated to be twice as in intact forests [START_REF] Cochrane | Fire science for rainforests[END_REF]. Furthermore, drought-related forest fires obviously release huge amounts of carbon into the atmosphere [START_REF] Grace | Perturbations in the carbon budget of the tropics[END_REF]): at the regional scale, [START_REF] Gatti | Drought sensitivity of Amazonian carbon balance revealed by atmospheric measurements[END_REF] showed that forest fires occurring during the extreme 2010 drought contributed to shift the annual carbon balance of the Amazon basin from a carbon-neutral status to a strong carbon release zone (0.48±0.18 Pg of carbon per year). In addition to the direct effect of fires on carbon balance, carbon losses from tree mortality in fire-affected forests have been shown to be cumulative through time, with an increase in large tree mortality three years after the fire event [START_REF] Barlow | Large tree mortality and the decline of forest biomass following Amazonian wildfires[END_REF].

Conclusions and research gaps

As synthetized here, a huge effort has been made over the past decade to improve our understanding of the response of tropical rainforest ecosystems to seasonal variations in precipitation and to extreme soil water conditions. The existing literature points to the adaptive capacity of these ecosystems to support seasonal droughts, but also to the great diversity and complexity of this response. The recent extreme drought events that occurred in these regions, the studies conducted in experimental droughts and the ongoing modelling studies allowed to greatly improve our knowledge when these ecosystems are pushed out of the soil water conditions during recurrent seasonal droughts. We now have better ideas about the potential limits for the carbon and water cycle and balance of these ecosystems to support extreme drought conditions. Our ability to model this response and simulate the potential consequences of future climate conditions has thus greatly improved, but large uncertainties, and even some discrepancies, still exist. This effort should thus be continuously supported, considering the major role played by these ecosystems at the global scale.

We have identified a number of research gaps to fill in the current knowledge on the response of these ecosystems to severe drought conditions. We highlight the most important below. These gaps require the international scientific community to combine efforts in order to conduct comprehensive studies in tropical rainforests on the three continents. These results are essential not only to simulate the future of these ecosystems but also to predict the future of the global earth carbon balance.

Taking combined stresses into account

An important point to consider is that the increase in the intensity and frequency of drought events will be accompanied by other changes in environmental conditions, such as increases in temperatures, vapour pressure deficit or atmospheric CO 2 concentrations. This review specifically targeted the effects of soil drought, but one must not lose sight of the consequences of other changes and of the potential feedback controls [START_REF] Malhi | Exploring the likelihood and mechanism of a climate-change-induced dieback of the Amazon rainforest[END_REF][START_REF] Cernusak | Tropical forest responses to increasing atmospheric CO 2 : current knowledge and opportunities for future research[END_REF]. [START_REF] Niinemets | Responses of forest trees to single and multiple environmental stresses from seedlings to mature plants: past stress history, stress interactions, tolerance and acclimation[END_REF] concluded that tree response to combined stresses, though none of them may be extreme separately, can be much greater than tree response to one single extreme stress. A concerted research effort should therefore be made in the near future to study combined effects. Modelling studies or large-scale manipulation studies combining soil drought, increase in CO 2 concentrations and temperature, or combining soil drought and nutrient levels should be encouraged in these forests to test the effect of these combined changes [START_REF] Cavaleri | Urgent need for warming experiments in tropical forests[END_REF].

Relating species-level and ecosystem-level responses to extreme droughts

Though we must maintain our research efforts, our understanding of tropical rainforest species vulnerability to drought has improved over the past decade. Ecosystem functioning depends on species composition and ecosystem response to drought results from each individual species response to drought. However, these responses do also depend on interactions among species (competition, facilitation), on interactions between species and their attendant microbial communities and on changes in species composition. Information about these interactions and changes is totally lacking. Manipulating species composition on large scales in these forests seems unrealistic, but building new models combining mechanistic and community dynamics approaches should help us understand the effects of climate changes on ecosystem functioning.

Understanding the role of microbial communities

There is evidence that plant resistance to drought is improved when fungal communities densely colonize the roots (e.g. [START_REF] Augé | Stomatal behavior of arbuscular mycorrhizal plants[END_REF]overview in Lehto and Zwiazek 2011). Yet, it has been shown that fungal community structure is strongly linked to tree species composition and tree species richness in tropical rainforests [START_REF] Peay | Strong coupling of plant and fungal community structure across western Amazonian rainforests[END_REF]. A change in tree species composition would thus influence fungal communities and their role in ecosystem functioning. Studies on the role of fungal communities in ecosystem functioning in tropical rainforests are very rare. A comprehensive study of these interactions is needed in order to understand the impact of seasonal drought and extreme drought events on belowground microbial communities and clarify their role in ecosystem functioning under climate changes.

Taking repetitive drought events into account

Most observations on the effect of drought on ecosystem functioning, with but a few exceptions, are based on a single drought event. The impact of repetitive events is still far from being understood, as is the resilience of tropical ecosystems to these events. [START_REF] Phillips | Drought-mortality relationships for tropical forests[END_REF] pointed out that the extreme 2005 drought in Amazonia was still affecting mortality rates in these ecosystems 2 years after the drought. How well these ecosystems can adapt to more frequent severe drought events [ENSO-related or others] in the future remains unknown. Is the resistance of tropical rainforest trees weakened by a first extreme drought event which subsequently increases their vulnerability? The recent occurrence of extreme drought events at low intervals in Amazonia or Asia brings interesting opportunities to study the effect of recurrent drought events in situ.

Assessing the adaptive potential of tropical rainforest tree species to droughts

Change in species composition is one way these ecosystems can naturally adapt to severe drought conditions, but functional adaptive mechanisms can also take place. One can wonder how far such adaptive mechanisms can go and when their limits will be reached. Tree tolerance to environmental stresses increases throughout ontogeny: over the next century, trees that are young today may well prove able to adapt to upcoming climatic conditions. However, how well tropical tree species will adapt to drought over the long-term is largely unknown. Among the strategies species use to survive drought conditions, carbon allocation deserves serious studies. A major gap exists in our knowledge concerning how carbon allocation patterns change in tropical rainforest trees under varying environmental conditions, though a few recent studies have provided interesting results: a clear asynchronism between leaf production and tree growth was observed [START_REF] Wagner | Asynchronism in leaf and wood production in tropical forests: a study combining satellite and ground-based measurements[END_REF]. This pattern has recently been linked with a different timing in carbon allocation between compartments [START_REF] Malhi | The productivity, metabolism and carbon cycle of two lowland tropical forest plots in south-western Amazonia, Peru[END_REF][START_REF] Rowland | Evidence for strong seasonality in the carbon storage and carbon use efficiency of an Amazonian forest[END_REF]. The authors also demonstrated different allocation patterns between the above-and belowground compartments. As an example, [START_REF] Rowland | Evidence for strong seasonality in the carbon storage and carbon use efficiency of an Amazonian forest[END_REF] showed a shift in the allocation of photosynthetic products from foliage and wood in the wet season to fine roots in the dry season. These allocation patterns are likely complex since they undoubtedly vary with drought intensity [START_REF] Brando | Drought effects on litterfall, wood production and belowground carbon cycling in an Amazon forest: results of a throughfall reduction experiment[END_REF][START_REF] Doughty | Allocation trade-offs dominate the response of tropical forest growth to seasonal and interannual drought[END_REF]. Comprehensive screenings on species variability in carbon and nitrogen allocation patterns should be conducted: they should include the consequences of both recurrent seasonal variations as well as extreme drought events.

Improving the ability of ecosystem or earth models to simulate drought responses

Even though a strong effort has been made in the last decade to include as many fine-scale functional processes as possible in mechanistic forest ecosystem models or earth models (e.g. [START_REF] Fisher | The response of an Eastern Amazonian rain forest to drought stress: results and modelling analyses from a throughfall exclusion experiment[END_REF][START_REF] Sakaguchi | Natural and drought scenarios in an east central Amazon forest: fidelity of the Community Land Model 3.5 with three biogeochemical models[END_REF][START_REF] De Weirdt | Seasonal leaf dynamics for tropical evergreen forests in a process based global ecosystem model[END_REF][START_REF] Powell | Confronting model predictions of carbon fluxes with measurements of Amazon forests subjected to experimental drought[END_REF][START_REF] Rowland | Evidence for strong seasonality in the carbon storage and carbon use efficiency of an Amazonian forest[END_REF], their ability to simulate the future response of tropical ecosystems to major drought events remains inadequate. In the context of climate change, large uncertainties on future carbon stocks or fluxes persist [START_REF] Poulter | Robust dynamics of Amazon dieback to climate change with perturbed ecosystem model parameters[END_REF]). These authors have identified research guidelines to improve the models, but to parameterize them, more observational and experimental data on the response of tropical ecosystems to drought events must be made available in concert. To improve simulations of climate change in the twenty-first century and its long-term effect on the ecosystem carbon balance, we should concentrate on phenology and mortality patterns and on CO 2 and other greenhouse gas fluxes among the different compartments in the ecosystem, particularly autotrophic respiration.

Evaluating the long-term impact of punctual extreme events

Most studies published so far have addressed the short-term consequences of extreme droughts; only very few (mainly experimental through-fall studies) have attempted to evaluate their long-term impact (Fig. 4). Despite their tremendous value in the study of response mechanisms, experimental studies cannot mimic the impact of successive, high-frequency major Fig. 4 Installation of an automatic weather station in the tropical rainforest in French Guiana (credits B. Hérault). Long-term monitoring of environmental conditions in remote forest inventory plots is a prerequisite to understand the effect of seasonal or extreme drought on tree and ecosystem functioning and simulate future changes droughts. The recent occurrence of several droughts in Amazonia and Asia with a return time lesser than 10 years may not give the forests time to completely recover between events and thus offers a major opportunity to evaluate the long-term impact of punctual extreme events. Remote sensing approaches provide the excellent tools to analyse these effects.

Fig. 2

 2 Fig.2The rainfall exclusion experiment in Caxiuanã National Forest Reserve, Brazil (credits L.Rowland)

  der Molen et al. 2011 and Shi et al. 2014 for a review). This decrease is largely explained by physiological [down-regulation of leaf, trunk or root gas exchange; decrease in heterotrophic respiration] or structural [leaf senescence, leaf shed] changes.

Fig. 3

 3 Fig.3The 55-m high eddy flux tower set up in 2003 in French Guiana[START_REF] Bonal | The impact of severe dry season on net ecosystem exchange in the Neotropical rainforest of French Guiana[END_REF]) (credits D. Bonal). Equipment installed on top of the tower (above the canopy) allows to continuously monitor the gas exchange (CO 2 , H 2 O) between the atmosphere and the considered ecosystem (around 50-100 ha)

Table 1

 1 List of through-fall exclusion experiments conducted in wet tropical or subtropical regions

	Site	Location	Climate	Period	Reference
	Daintree rainforest	Australia	Seasonal wet tropical	2013-	http://www.jcu.edu.au/daintree
	Caxiuanã National Forest Reserve	Brazil	Seasonal wet tropical	2002-	Fisher et al. (2007)
	Tapajós National Forest	Brazil	Seasonal wet tropical	2000-	Nepstad et al. (2002)
	Lore Lindu National Park	Indonesia	Aseasonal wet tropical	2007-2009	Van Straaten et al. (2011)
	FazendaVitória	Brazil	Seasonal wet tropical	1993-1996	Cattânio et al. (2002)
	Luquillo Experimental Forest	Puerto Rico	Aseasonal wet subtropical	2009	Wood and Silver (2012)
	Golfo Dulce Forest Reserve	Costa Rica	Seasonal wet tropical	2007-2008	Cleveland et al. (2010)

D.Bonal et al.

Acknowledgments This review was stimulated by discussions conducted during a meeting in Toulouse in 2014 funded by an Investissement d'Avenir grant from the ANR (CEBA: ANR-10-LABX-0025). We thank all the participants in this meeting who contributed to these discussions. We thank S. Lewis (University of Leeds, UK) for the rights to include Fig. 1 in this review and L. Rowland (University of Edinburgh, UK) for sharing recent pictures of the rainfall exclusion experiment in Caxiuanã, Brazil (Fig. 2).

Funding CS was supported by a grant from the "European Research Council Synergy", grant ERC-2013-SyG-610028 IMBALANCE-P. FW was supported by a grant from the "Fundação de Amparo à Pesquisa do Estado de São Paulo", Brazil, grant 13/14520-6.