Research Article

North America’s oldest boreal trees are more efficient water users due to increased [CO2], but do not grow faster

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PNAS February 12, 2019 116 (7) 2749-2754; first published January 28, 2019; https://doi.org/10.1073/pnas.1816686116

  1. Edited by Donald R. Ort, University of Illinois, Urbana, IL, and approved December 20, 2018 (received for review September 27, 2018)

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Significance

The metabolism of North America’s oldest boreal trees (Thuja occidentalis L.) is strongly affected by rising anthropogenic CO2 emissions. Intrinsic water use efficiency (iWUE) increased dramatically, although nonlinearly, since the beginning of the industrial Era. Our study shows that while T. occidentalis L. acclimated to rising [CO2], no stem growth was observed, suggesting that trees could not benefit from the increased iWUE.

Abstract

Due to anthropogenic emissions and changes in land use, trees are now exposed to atmospheric levels of [CO2] that are unprecedented for 650,000 y [Lüthi et al. (2008) Nature 453:379–382] (thousands of tree generations). Trees are expected to acclimate by modulating leaf–gas exchanges and alter water use efficiency which may result in forest productivity changes. Here, we present evidence of one of the strongest, nonlinear, and unequivocal postindustrial increases in intrinsic water use efficiency (iWUE) ever documented (+59%). A dual-isotope tree-ring analysis (δ13C and δ18O) covering 715 y of growth of North America’s oldest boreal trees (Thuja occidentalis L.) revealed an unprecedented increase in iWUE that was directly linked to elevated assimilation rates of CO2 (A). However, limited nutrient availability, changes in carbon allocation strategies, and changes in stomatal density may have offset stem growth benefits awarded by the increased iWUE. Our results demonstrate that even in scenarios where a positive CO2 fertilization effect is observed, other mechanisms may prevent trees from assimilating and storing supplementary anthropogenic emissions as above-ground biomass. In such cases, the sink capacity of forests in response to changing atmospheric conditions might be overestimated.

Plants are an integral component of both water and carbon cycles on Earth. This is because stomata (i.e., microscopic apertures on plant leaves) allow plants to adjust their metabolism to changing environmental conditions by controlling the tradeoff between CO2 intake for photosynthesis and water loss through transpiration. However, since the beginning of the industrial period, anthropogenic emissions and changes in land use resulted in a 40% increase in atmospheric [CO2] (1) (hereafter referred to as ca). Plants have not been exposed to concentrations above 290 ppm for at least 650,000 y (2, 3), so the dynamic carbon–water coupling that prevailed for several millennia could be disrupted with potential, yet uncertain, impacts on hydro-ecosystem functioning (4, 5).

One of the most striking consequences of elevated ca is an increase in plant intrinsic water use efficiency (iWUE, i.e., the rate of carbon uptake per unit of water lost). The rate of increase of iWUE in response to rising ca depends on how the assimilation rate (A) and/or stomatal conductance (gs) adjusts to determine the optimal internal [CO2] (ci) (5, 6). Three theoretical scenarios (hereafter referred to as S1–S3) have been proposed (7) as guidelines on how to interpret possible acclimation strategies and their respective effects on iWUE (Fig. 1). In S1, plants maintain a constant ci (iWUE increases strongly); in S2, there is a constant ci/ca ratio (iWUE increases moderately); and in S3, there is a constant difference between ca and ci (iWUE remains constant). Short-term flux measurements (4) and free-air CO2 enrichment (FACE) experiments (8) have shown that S1 requires a strong and active physiological response leading to the highest rates of iWUE increase, most consistent with a strong CO2 fertilization effect. However, the active iWUE response documented over short periods of time (yearly to decadal) may not reflect the changes occurring on longer timescales characteristic of natural forests (decadal to centennial). Over these timescales, there is no clear line of evidence that points toward a single, timescale-independent, acclimation strategy. To the contrary, the emerging concept of “optimal stomatal behavior” implies that woody plants shift along a continuum of strategies (5) and adjust gs to maximize carbon gains while minimizing exposure to drought stress. This complex interplay takes place on yearly to multidecadal timescales and therefore requires the investigation of time series that are sufficiently long to be able to track and compare present-day stomatal behavior and iWUE changes to preindustrial reference levels.

Fig. 1.
Fig. 1.

Evolution of iWUE, ca, RWI, and δ18O since 1300 CE for old-growth white cedars at lake Duparquet, Eastern Canada. Two distinct periods emerge which have been highlighted through different coloring and shading: P1 (1850–1965, red) and P2 (1965–2014, green). (A) iWUE is calculated from δ13C-derived physiological parameters shown in Fig. 2. The gray shading around the iWUE curve represents the intertree variability. The three theoretical iWUE scenarios presented in the Introduction (S1, constant ci; S2, constant ci/ca; and S3, constant ca − ci) are plotted as dotted lines. (B) Annually resolved RWI chronology, RCS standardized with bootstrap 95% CI (gray shading). (C) δ18O values.

Moreover, it is still unclear how these shifts in stomatal behavior impact forest productivity, i.e., whether changes in the rate of increase in iWUE are mirrored by changes in growth rates. Based on FACE studies (8), one could hypothesize that increases in iWUE (e.g., S1 or S2) would enhance stem growth. However, at least in boreal North America, tree-ring–based and bioclimatic modeling studies found little evidence of a widespread growth of forest stands that could be attributed to ca increases (9, 10). Conversely, in this zone, growth has declined over vast portions of land, which has been attributed to the negative effects of temperature-induced droughts (10, 11). However, few of these tree-ring studies were accompanied by a thorough and time-continuous investigation of changes in gas exchange in response to increasing ca. Only one study measured changes in iWUE and found that the positive response to ca could not compensate for growth declines observed at the southernmost fringe of the boreal forest (12). Nevertheless, a high level of uncertainty persists with regard to the linkages between climate variability, iWUE, and forest productivity and their changes since preindustrial times.

To remedy this uncertainty, we report on the acclimation of a population of long-lived white cedars (Thuja occidentalis L.) growing in xeric conditions that offers a unique, long-term perspective on iWUE–growth relationships. We present a long (1300–2014), annually resolved, multiproxy tree-ring chronology in eastern North America (ring widths and stable isotopes of carbon and oxygen), to track changes in iWUE and growth attributable to rising ca and climate variability for a period that extends far beyond the onset of the Industrial Era.

Results and Discussion

Acclimation to Rising ca.

Our results indicate a remarkable and unprecedented (59%) iWUE increase over the past 150 y (Fig. 1A). δ13C-derived physiological parameters reveal that old-growth white cedars have been acclimating to rising ca in two distinct stages: period 1 (P1: 1850–1965, red shaded area in Fig. 1) and period 2 (P2: 1965–2014, green shaded area). During P1, a 37.42-ppm increase in ca was accompanied by a slight and nonsignificant (P> 0.05) 1.84-ppm increase in ci (Fig. 2 and SI Appendix, Table S1). This translates into a 28% iWUE increase compared with preindustrial (1300–1850) averages. Thus, during P1, for each increase of ca of 1 ppm, ci rose by only 0.05 ppm. This response nearly matches predictions from S1 according to which ci would remain constant for increasing ca (see Introduction for details) (Fig. 1A). Once ca reached 320 ppm (onset of P2), ci started to rise proportionally to ca (Fig. 2), resulting in a constant ci/ca ratio of 0.49 (SI Appendix, Table S1), accompanied by an additional 31% increase in iWUE (in agreement with S2).

Fig. 2.
Fig. 2.

Tree-ring δ13C (corrected for Suess effect), derived physiological parameters (δ13C, ci, ci/ca, Δ, ca−ci, iWUE plotted against ca. The scatter plot is divided into three periods: preindustrial (black, <1850), P1 (red, 1850–1965), and P2 (green, 1965–2014). Linear trends describing the evolution of physiological parameters as a function of ca are depicted for P1 and P2. Thick lines represent significant (P< 0.05) increasing or decreasing trends.

The observed rate of iWUE increase during P1 (0.59 μmol⋅mol−1 per ppm of ca) is among the highest ever reported for the Northern Hemisphere (13⇓⇓⇓–17). Thus, even at a mature age, white cedars can actively respond to rising ca, by maintaining a constant ci. Around the world, evidence from tree-ring analyses to support the hypothesis of a constant ci (S1) exists, but is scarce. Prosopis alba (Griseb.) trees from the Atacama Desert (Chile) maintained a constant ci from 1890 (earliest date in study) to 1980 (18). A population of Smith fir (Abies georgei var. smithii) trees of the southeastern Tibetan plateau in China (19) presented a constant ci (150 ppm) from 1900 (earliest date in study) to 1944. In Finland, all beech, oak, and pine species also revealed a relatively constant ci from 1895 (earliest date in study) to 1975 (20). At our site, once ca reached 320 ppm, the rate of increase of iWUE slowed down to 0.31 μmol⋅mol−1 per 1 ppm of ca, marking the beginning of P2 and a lower sensitivity to increasing ca. While uncommon, similar shifts from a near-constant ci to a proportional increase of ci with rising ca have been observed in relatively arid (19) and temperate areas (20), but were never reported in boreal North America.

A shift in the acclimation strategy to rising ca implies active physiological adjustments, either through carbon assimilation rate, A, or stomatal conductance, gs, or both (5). To determine the relative importance of each factor for δ13C-derived iWUE in white cedars, we used a tree-ring δ18O analysis. According to the dual-isotope theory (21), the δ18O composition of tree rings is unaffected by photosynthetic activity (22) and more influenced by source-water composition, isotopic exchanges with plant tissues, and evaporative enrichment of leaf water (23, 24). Our year-resolving tree-ring δ18O time series (Fig. 1C) shows no correlation with δ13C values (P> 0.05) and does not follow the increases in iWUE observed after 1850. Up to 1965, δ18O remains relatively constant while δ13C continually increases (SI Appendix, Fig. S11), suggesting that stimulation of A by increased CO2 may be responsible for the pronounced increase in iWUE during P1. After 1965 (P2), however, mature T. occidentalis L. probably switched from an A-dominated to a gs-dominated iWUE response. A steady increase in both δ18O and iWUE which persists until the end of our time series indicates a declining stomatal conductance and transpiration, which is typically accompanied by enrichment in leaf water with 18O due to the preferential evaporation of lighter oxygen isotopes (24).

Ultimately, our study provides in situ evidence of a shift in stomatal behavior: Old-growth white cedars maximized carbon gains at low ca (during P1), but minimized water losses and exposure to drought stress at higher ca (during P2). This switch in acclimation strategy is coherent with the one proposed by the optimal stomatal behavior theory (5). Indeed, based on a large number of field and [CO2]-enrichment studies, the theory suggests that as ca increases, no fixed homeostatic set point is observed in tree acclimation. Thus, at low ca, plants seem to be profligate water users, as incremental increases in gs lead to significant carbon gains. However, at high ca, saturation of the photosynthetic apparatus forces the switch to a drought-avoidance strategy, because incremental increases in gs lead to water losses that are disproportionately large relative to carbon gains. In conformity with that theory, we postulate that the shift from P1 to P2 indicates that white cedars are getting closer to saturation with rising ca. iWUE of white cedars will thus continue to increase in the near future, but at half the pre-1965 rate.

Contributions of ca and Climate to iWUE Variability.

Commonality analysis revealed that both ca and climate predictors [growing season (May–August) average air temperatures (T), soil moisture index (SMI), and vapor pressure deficit (VPD)] had a significant effect on iWUE during the 1953–2014 period. However, each variable had its maximal effect at a different time frequency. To show this, we incrementally filtered out the lower-frequency component of iWUE, each time computing a new commonality analysis (Materials and Methods). While the lower-frequency bands (f) between 0 cycle⋅y−1 and 0.03 cycle⋅y−1 (cycle lengths between ∞ and 75 y) were incrementally removed, ca explained 75% ± 9% of the variance in iWUE and beta weights remained very high (0.9 ± 0.03) (Fig. 3 A and B). About 20% of the overall effect of ca on iWUE also appeared to be shared with that of other climatic variables, namely VPD and T (Fig. 3 C, 1). As the degradation of the iWUE signal continued, ca quickly became less dominant and the importance of climate predictors progressively increased. For example, filtering out the low-frequency component of iWUE up to f = 0.05 cycle⋅y−1 (cycle lengths = 20 y) boosted beta weights and proportion of variance explained by climate predictors to a point that exceeds those of ca (Fig. 3 A and B). More specifically, the pure (positive) effect of summer VPD at higher frequencies (cycle length = 20 y) rose to nearly 20% (±6%), while ca had no more effect on iWUE at those timescales (Fig. 3 C, 2).

Fig. 3.
Fig. 3.

(A and B) Commonality analysis showing beta weights (A) and the proportion of variance (B) in iWUE explained by the pure effects of ca (gray) and growing-season (May–August) temperatures (T, blue), VPD (green), and SMI (red). Color bands represent the bootstrap 95% CIs for beta weights and proportion of variance explained in iWUE. (C) Pure and shared effects are detailed for two specific iWUE frequencies: f = 0.013 (75 y) (C, 1) and f = 0.125 (8 y) (C, 2).

While most of the variance in iWUE can be explained by low-frequency variations in ca, climate variables influence iWUE at the higher end of the frequency spectrum. The strong relationship between ca and low-frequency changes in iWUE could somehow be expected because variations in iWUE are physiologically linked to ca (25). At higher frequencies though, VPD, an important driver for transpiration, plays a slightly more important role in controlling iWUE, as documented for other species and environments (26). This implies that at annual to subdecadal timescales, increases in VPD led to reductions in stomatal conductance and increases in iWUE during the growing season (27).

The unprecedented increase in iWUE since 1850, however, cannot be attributed to changes in climate. For example, hypothesizing that the iWUE increase was climate induced would imply that increasingly dry conditions would have prevailed, causing a sustained stomatal closure and a drastic increase in iWUE. However, no such clear trend has been found in climate records extending back to 1901 (SI Appendix, Fig. S13). The pre-1965 period actually shows increasingly wetter/colder growing seasons (lower T and higher SMI). These pre-1965 trends seem to be confirmed by several independent dendrochronological indicators that point toward a decrease in the intensity and frequency of droughts in the area: The amount of biomass being burned in northwest Quebec has decreased since 1930 (28, 29), water levels of lake Duparquet have been rising since 1850 (30), and an increase in the severity of spring floods has been reported during that period (31). Growing-season climate conditions became drier/hotter only after 1965 (T increased, SMI decreased, and VPD increased).

As trees have been acclimating to rising ca levels since the beginning of the Industrial Era, it appears plausible that climatic factors played only a marginal and indirect role in the observed interdecadal variability in iWUE. The strong stimulation of photosynthesis during P1 needed to rely upon a high stomatal conductance that probably would not have been possible if drier conditions prevailed. In contrast, the drier post-1965 climate conditions probably reinforced the drop in stomatal conductance during P2, therefore down-regulating photosynthesis and the rates of iWUE increase. In combination with the progressive saturation of the photosynthesis apparatus, this drying trend might represent an additional contributing factor that triggered the switch to a constant ci/ca (S2) acclimation strategy during P2.

No Unprecedented Growth Despite Increasing iWUE.

Given the significant increase in iWUE, it appears reasonable to expect that white cedars experienced a substantially higher growth since 1850. However, our analysis of ring-width indexes (RWIs) shows that growth during the last 150 y was good, but not unprecedented at the scale of the last 715 y (Fig. 1B). Indeed, since 1300, at least three periods (early 1400s, 1520s, and mid-1800s) are equivalent in magnitude to the periods of high growth during the late 1980s–early 1990s.

Several studies have reported iWUE increases without apparent growth stimulation (13, 32⇓⇓–35). However, most of these studies found only modest average increases in iWUE (20% over the past 40 y) (32), reflecting a constant ci/ca adjustment (S2). Observed increases in growth that can be attributed to ca (19) remain scarce and are inconsistently distributed across the Earth’s biomes (32). The same holds for boreal Canada where only few measurements of iWUE are available and tree-ring widths provide little evidence for a positive growth trend that could be interpreted as a CO2 –related stimulation of photosynthesis (9, 10, 13). White cedars typically found in mesic and hydric sites around Lake Duparquet even exhibited a notable growth decline during recent decades (36).

Four mechanisms can explain the lack of growth stimulation in a context of increasing iWUE. First, carbon allocation strategies might have shifted with time. Indeed, for slow-growing and water-stressed trees such as white cedars, priority in carbon allocation might be given to storage components other than the stem (which is used here as a proxy for growth). Under such conditions, a greater proportion of photosynthates would be used to produce volatile organic compounds or root exudates instead of above-ground biomass (37). Carbon taken up allocated to biosynthesis may also have been lowered owing to respiratory requirements for acquiring water and nutrients (38, 39). Second, the lack of growth stimulation in a context of increasing iWUE has often been associated to drought stress (13, 17, 33, 35). While we could not find any evidence for a persistent, century-long, drying trend (SI Appendix, Fig. S13), commonality analysis revealed that the RWI is positively (but poorly) related to the summer SMI (total effect <20%; SI Appendix, Fig. S11), implying that lateral growth could be limited when dry conditions prevail (40), especially during P2. Third, a progressive reduction in stomatal density (41) could also result in a rise of iWUE at the stomata scale without significant increase of total photosynthesis at the tree level. Higher CO2 uptake by stomata co-occurring with a lower number of stomata would lead to carbon gains similar to the ones that prevailed during the preindustrial period. However, there should be a lower limit for stomatal density as scaled leaves need evaporative cooling and efficient CO2 diffusion to the chloroplasts. Finally, nutrient limitation (42) also needs to be considered as a potential factor limiting growth in these thin-soiled, xeric environments. For example, in similar ecological conditions in southeastern Canada, ref. 43 found that phosphorus was the main limiting nutrient for slow-growing white cedars (apart from the limited physical space for root penetration in bedrock). An increase in leaf and root (but not trunk) biomass was observed in young white cedar saplings when supplied with additional phosphorus (43).

Our study has important implications for the modeling of vegetation response to atmospheric variability. Most ecophysiological and dynamic global vegetation models (DGVMs) predict an increase in plant biomass due to a stimulation of photosynthesis by ca (44). Given the results presented here, such models might overestimate future forest carbon storage capacities. Our post-1850 data showed an unprecedented increase in iWUE that coincided with a drop in carbon use efficiency. These results imply that even when a marked stimulation of photosynthesis drove changes in iWUE (at least until 1965), the above-ground biomass did not increase substantially. Therefore, in light of previous findings (32), any assumption that positive stimulation of photosynthesis by CO2 systematically translates into more carbon storage should be treated with caution. This result has wide-ranging implications for the modeling of climate–carbon feedbacks at the leaf–atmosphere interface and stresses the urgent need for additional research in this area to reduce these uncertainties.

Conclusions

North America’s oldest boreal trees (T. occidentalis L.) exhibited an unprecedented 59% increase in iWUE since the beginning of the Industrial Era, mainly in response to rising atmospheric [CO2] (ca). This response was not constant in time, but a clear regime shift occurred around 1965, gradually switching the leaf gas-exchange strategy from a constant ci to a constant ci/ca acclimation. Trees maximized carbon gains between 1850 and 1965 (P1) when the local climate was relatively wet and cold. Conversely, they reduced vulnerability to drought stress when the local climate became hotter and drier after 1965 (P2), possibly also combined with a closer saturation of the photosynthetic apparatus. However, the marked iWUE increase since 1850 did not translate into enhanced stem growth. This implies that other physiological processes such as nutrient availability, changes in carbon allocation strategies, or changes in stomatal density may have offset the growth benefits awarded by the increase in iWUE. Our results thus suggest that even in favorable conditions for growth, not all trees can take advantage of elevated levels of ca and iWUE. These mechanisms are not typically taken into account by ecophysiological models (45) and DGVMs (44) which may lead to them overestimating any positive effects bestowed by a higher ca on carbon assimilation and fixation. Predictions of elevated future growth and possible alleviating effects on ca might be overly optimistic if the models do not allow for the possibility of constant or even reduced growth in the context of increasing ca. It would be advisable to define improved allocation rules and determine whether those rules can change over time (and with increasing ca). Integrating measurements acquired at shorter time intervals (daily or weekly resolution) with long times series of tree-ring measurements would further help to track and define those allocation rules in trees exposed to a varying climate and nutrient availability.

SI Appendix.

SI Appendix provides complementary information on methods and results: the regional curve used for regional curve standardization (RCS), quality statistics for the RCS chronology, cohorts selected for δ13C and δ18O analysis and their junction, effect of correction methods on δ13C chronology, and results for whole-wood and cellulose δ13C and δ18O values comparison.

Materials and Methods

Study Site and Sampling Strategy.

Lake Duparquet is located at the southern limit of the boreal forest (48,47° N, 79,27° W), in northeastern Canada (SI Appendix, Fig. S1). Climate is continental, cold, and humid, with a mean annual temperature of 1°C and a mean annual total precipitation of 985.2 mm (climate normals for 1981–2010 from Station Mont-Brun, located 12 km south and 42 km east from Duparquet) (46). In 1987, 39 trees were sampled by ref. 40. To extend their ring-width chronology (1186–1987) until 2014, 35 trees, spread across five islands and six peninsulas of Lake Duparquet (SI Appendix, Fig. S1), were resampled in 2012 and 2014 using a 5-mm core increment borer at chest height. Sixteen trees were also part of the first chronology by ref. 40. Trees were measured, cross-dated, and detrended using the RCS approach (47) (SI Appendix).

Stable Isotope Chronologies.

Eleven trees were selected for carbon and oxygen stable isotope ratio analysis to cover the maximum time period with the smallest number of possible cohort changes (SI Appendix, Fig. S4). This avoids loss of a reliable mean as we go back in time, considering the systematic offsets typically encountered in the stable isotope analyses of different trees (25, 48, 49). Isotope chronologies have been shown to require few replicates (as little as four) to obtain a strong common signal (expressed population signal ≥0.85) (25). Two cohorts of six (cohort 1: 1620–2014) and five trees (cohort 2: 1295–1645) were selected, with an overlap of 25 y (SI Appendix, Fig. S4). The trees selected for stable isotope analysis had different ages that were well spread through time. This avoids incorporating noise due to nonclimatic age effects (SI Appendix, Fig. S4). The first 50 y of each sample were excluded to avoid any nonclimatic age-related trends (49, 50) (SI Appendix).

δ13C-Derived Physiological Parameters.

δ13C variability in tree rings depends on processes by which trees fractionate carbon at the leaf gas-exchange site (discrimination against 13C vs. 12C) before fixing it in the stem during the growing season (25, 51). Carbon fractionation (Δ, ‰) is expressed as the difference between δ13C values of atmospheric CO2 (δ13Cair) and tree-ring δ13C values (δ13Ctree) as shown by Eq. 1 (7):Δ(‰)=δ13Cair−δ13Ctree1+δ13Ctree/1,000≈δ13Cair−δ13Ctree.[1]Carbon fractionation thus occurs in two main steps (52): CO2 diffusion through stomata (step i ≈ −4.4‰; ref. 53) and carboxylation (step ii ≈ −27‰; refs. 25 and 54). However, the overall fractionation is dependent on the ratio between leaf intercellular (ci) and ambient (ca) CO2 concentrations:Δ≈δ13Cair−δ13Ctree=a+(b−a)cica.[2]

Records of δ13Cair and ca obtained from Antarctic ice cores by ref. 55 were linearly interpolated until 1295. From 1850 to 2003, values from ref. 25 were used (following refs. 2, 4, and 55) and linearly interpolated until 2014.

Based on plant physiology theory and models, physiological parameters can be derived from tree-ring δ13C values. ci is calculated from Eq. 2, provided that all other variables are known. iWUE, a measure of the amount of carbon assimilated per unit leaf area per unit time per unit cost of water, is calculated as (18)iWUE=Ags=ca−ci1.6.[3]According to Eq. 3, the difference between ca and ci is proportional to iWUE and reflects the balance between the rate of CO2 assimilation (A) and stomatal conductance (gs).

For each of the three theoretical scenarios of leaf–gas strategy (7), the δ13C response to ca is shown in Fig. 2 (main text). This was achieved by fixing ci accordingly, using Eq. 3. Scenarios start in 1850, at the beginning of the industrial period, and exhibit a linear response to ca increases and assume a negligible ci response to climate variability. The ci preindustrial level was 150 ppm (the 1295–1850 mean).

Dendroclimatic Analyses.

Daily weather data (1901–2014 maximum and minimum temperatures) and precipitation (1901–2014 sum) and VPD (1953–2014) were retrieved from BioSIM v.10, which interpolates site-specific estimates from historical weather observations (56) as described in ref. 57. The quantity of available soil moisture was estimated for each month using the quadratic + linear (QL) formulation procedure described in ref. 58, which accounts for water loss through evapotranspiration (simplified Penman–Monteith potential evapotranspiration) and gain from precipitation. Parameter values for maximum and critical available soil water were set at 300 mm and 400 mm, respectively; the number of weather stations for interpolation was set to eight. We used values of annual mean ca recorded at Mauna Loa observatory since 1958 (59); the data were extended to 1901 using estimates from ice cores (60).

Commonality analysis (61) was used to explore the climate effects of ca and climate predictors on iWUE, δ18O, and RWI. With a commonality analysis, one seeks to decompose linear regression R2 into its unique and common effects. Unique effects indicate how much variance is uniquely accounted for by a single variable, taken as a single predictor. Common effects indicate how much variance is common to a set of predictors. Total effects refer to the combination of unique and common effects and describe the explanatory power of a predictor, summing up all commonalities. Commonality analysis is particularly useful to estimate effects in the presence of multicollinearity in a predictor dataset. For each analysis, we show regression beta weights, unique effects, common effects, and total effects for each variable, as well as R2 values for the whole regression model. For simplicity, we chose to use a limited set of predictor variables: May–August (growing season) temperatures (T), SMIs, and VPDs. We performed the commonality analysis iteratively; i.e., the data were passed several times through a high-pass filter which led to incremental degradation of the original iWUE variable, as each pass removed a bigger part of the low frequencies. Hence, at the beginning of the loop iWUE contained all frequencies from 0 ≤f≤ 0.5 y−1 (cycle lengths between ∞ and 2 y) while at the end of the iteration iWUE was degraded to a perfectly detrended seesaw signal with f = 0.5 y−1 (cycle length = 2 y). The iterative degradation of the original iWUE signal coupled to the commonality analysis allowed us to pinpoint those frequencies above or below which ca and climate had a dominant influence on iWUE, δ18O, and RWI.

Acknowledgments

We acknowledge the contribution of many people who helped with field and laboratory work: A. Barbe, G. Proulx, P. Leclerc, M. Gratton, and A. Adamowicz-Walczak. We thank the Natural Sciences and Engineering Research Council (NSERC) and Her Majesty The Queen in due right of Canada. C.G.-C. acknowledges financial support from both NSERC and Fonds de Recherche Québécois Nature et Technologies for her master’s thesis.

Footnotes

  • ↵1C.G.-C. and É.B. contributed equally to this work.

  • ↵2To whom correspondence should be addressed. Email: boucher.etienne{at}uqam.ca.

  • Author contributions: C.G.-C., É.B., Y.B., I.D., and M.G. designed research; C.G.-C., É.B., and M.P.G. performed research; C.G.-C., É.B., M.P.G., and J.-F.H. contributed new reagents/analytic tools; C.G.-C., É.B., Y.B., M.P.G., I.D., L.C.R.S., and J.-F.H. analyzed data; C.G.-C., É.B., Y.B., M.P.G., I.D., L.C.R.S., and J.-F.H. wrote the paper; and É.B. provided funding.

  • The authors declare no conflict of interest.

  • This article is a PNAS Direct Submission.

  • This article contains supporting information online at www.pnas.org/lookup/suppl/doi:10.1073/pnas.1816686116/-/DCSupplemental.

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North America’s oldest boreal trees are more efficient water users due to increased [CO2], but do not grow faster
Claudie Giguère-Croteau, Étienne Boucher, Yves Bergeron, Martin P. Girardin, Igor Drobyshev, Lucas C. R. Silva, Jean-François Hélie, Michelle Garneau
Proceedings of the National Academy of Sciences Feb 2019, 116 (7) 2749-2754; DOI: 10.1073/pnas.1816686116
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