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Correspondence: Gabriela Gleiser (email@example.com)
Artificial selection and genetic engineering plus an expanding repertoire and use of agrochemical inputs have allowed a rapid and continuous increase in crop yield (i.e., volume production per unit area) over the last century, which is needed to fulfill food demands from a growing human population. However, the first signs of yield deceleration and stagnation have already been reported for some globally important crops. Therefore, the study of the drivers of yield growth and its variation is essential for directing research and policies aiming at ensuring food security in the forthcoming years. We used data on mean and variability in annual yield growth for 107 globally important crops to assess the role of environmental (i.e., climatic region) and plant intrinsic traits (i.e., type of harvested organ, pollinator dependence, and life form) as drivers of change in yield growth and its stability. We applied a comparative approach to control for biases associated with phylogenetic non-independence among crops, an approach rarely used in agronomic studies. Average yield growth and its variation were not phylogenetically structured. Yield growth decreased with increasing pollinator dependence in tree crops but not in herbaceous and shrubby crops. Interannual yield variation tended to increase with increasing pollinator dependence, and it was higher in crops from temperate regions, in those cultivated for their reproductive organs, and in tree and shrubby crops as compared with herbaceous ones. Information on ecological correlates of crop yield growth and interannual yield variation can be used in the design of more sustainable and diversified agriculture schemes.
Human population is increasing steadily, imposing greater demands on agricultural production (Godfray et al., 2010; Foley et al., 2011). Replacement of natural habitats by croplands, advances in crop breeding programs and genetic manipulation, a wider repertoire and more intensive use of agrochemicals (including pesticides, fungicides, herbicides, and fertilizers), and a widespread adoption of increasingly sophisticated irrigation systems have all allowed a rapid growth in total crop production and crop production per unit area (i.e., crop yield) during the last century (Miflin, 2000). This growth in yield has played a central role in fulfilling increasing food demands (Tilman et al., 2002; Aizen and Harder, 2009). However, human food security depends not only on crop yield but also on its interannual variation, which can slow down yield growth (Garibaldi et al., 2011), affecting food prices and limiting people's access to a broad nutritional diet, especially in developing countries (Ray et al., 2015; Schauberger et al., 2016). Indeed, first signs of yield deceleration and stagnation have already been reported for some globally important crops (Ray et al., 2012; Iizumi et al., 2014). In this context, bringing a comparative (i.e., including several species), ecological perspective into the crop science field can be crucial to broaden our knowledge of the factors limiting crop yield. More specifically, a phylogenetically framed approach is essential to avoid statistical biases associated with phylogenetic non-independence due to shared evolutionary history among crops (Revell, 2010; Symonds and Blomberg, 2014) and, thus, to accurately identify global drivers and correlates of crop yield growth and growth stability (i.e., the inverse of interannual yield variation). Proper identification of these ecological drivers and correlates can be useful in designing national and supra-national policies aiming at guarantying food security in the forthcoming years. Yet, such an approach has been rarely applied in studies on crop biology (Kantar et al., 2015; Milla et al., 2015; Milla et al., 2018; Martin et al., 2019).
Plant growth depends directly on the photosynthetic rate, which is influenced by temperature as well as by light, water, and soil nutrient availability (Schulze et al., 2019). Therefore, all else being equal, tropical and subtropical crops might have higher yield growth than temperate crops because the effect of temperature on plant growth may impose an upper limit on yield in temperate zones. In addition, more pronounced daily and seasonal temperature fluctuations at higher latitudes, including the occurrence of frosts (Rodrigo, 2000), might predict lower crop yield stability. Furthermore, low solar radiation may affect soil nutrient uptake (Schauberger et al., 2016), reducing the potential for yield growth at higher latitudes. However, plant growing conditions may not be so benign in the tropics. For instance, an excess of solar radiation towards lower latitudes could be detrimental for plant development because of increasing damage risk of the photosynthetic systems (Schauberger et al., 2016; Tan et al., 2020). Also, tropical soils in humid areas suffer from intense rainfall and nutrient lixiviation, often becoming nitrogen and phosphorous limited, and thus are commonly less productive than soils in temperate regions (Santiago, 2015; Jeffery et al., 2017). Moreover, indirect climate effects, via higher weed growth and pest occurrence, can also hamper yield growth at lower latitudes (Rosenzweig and Liverman, 1992). Hence, differences in yield growth and yield variability between tropical and temperate crops, if any, might provide first cues to the relative importance of climatic factors as proximate and ultimate modulators of the growth rate in crop productivity.
Fruit and seed production rely on available resources (i.e., fixated carbon, nitrogen, phosphorous, etc.) once investment in vegetative growth and maintenance is secured (Lacey, 1986; Obeso, 2002; Weiner et al., 2009; Tuller et al., 2018); on different pollen vectors like wind, in wind-pollinated plants; and on a diversity of animal pollinators, in pollinator-dependent plants (Willmer, 2011). Consequently, given the expected higher unpredictability associated with the production of reproductive organs, we might predict lower average yield growth and higher yield variability in those crops cultivated for their reproductive parts (i.e., either seeds or fruits) than in those cultivated for their vegetative parts (e.g., tubers, stems, leaves).
Among those crops that are cultivated for their reproductive parts, there is also a broad variability in pollinator dependence (Klein et al., 2007; Aizen et al., 2019), ranging from crops that are completely independent of animal pollinators (e.g., bananas, olives, walnuts, wheat) to crops that are completely dependent on pollinators (e.g., cocoa, kiwi, vanilla, watermelon). Globally, ∼75 % of the crops depend, to different degrees, on both wild and managed pollinators for seed and/or fruit quantity and/or quality maximization (Klein et al., 2007; Garibaldi et al., 2013; Rader et al., 2016). Because of evidence that wild and managed pollinator populations are declining in many regions (Potts et al., 2010) and that pollinator availability varies naturally over space and time (Horvitz and Schemske, 1990; Price et al., 2005), crops that rely more strongly on pollinators are expected to be more susceptible to pollinator shortages. Accordingly, Garibaldi et al. (2011) reported that crops that depended more heavily on pollinators had lower mean yield growth and lower yield stability. However, phylogenetic non-independence among crops was not accounted for, and the potential roles of more direct, confounded effects and interactions with associated factors were not evaluated.
Relative investment in reproduction also relates to plant growth form. Annual plants invest a large proportion of their total resource budget in reproduction during a single season, whereas shrubs and specially trees are long lived and make large investments to develop long-lasting supportive and protective tissues (Petit and Hampe, 2006; Weiner et al., 2009), even before any resources are devoted to reproduction (Harper, 1977; Kozlowski and Uchmanski, 1987). Also, fruit and seed production in long-lived plants are usually characterized by high interannual variation (i.e., masting) that is often determined by the overall plant's resource availability as affected by the environment, and possibly by intrinsic resource accumulation–depletion cycles (Bogdziewicz et al., 2019). Thus, genetic or cultivation improvements are probably reflected in faster and more constant yield growth in annual crops as compared to shrubs and trees, which have longer life cycles and more complex patterns of resource allocation (Cheplick, 2005).
Crop species sharing a common recent ancestor may also show more similar yield growth just by descent. Indeed, significant phylogenetic signal has been reported in traits related to photosynthesis and plant growth (Zheng et al., 2009). Therefore, any analysis of crop yield growth and stability involving several crops should be evaluated within a phylogenetic context. Furthermore, because environmental and plant intrinsic traits do not act independently, the evaluation of possible interactions between them is fundamental. For example, as previously mentioned, lower yield stability was reported for those crops that depend more heavily on pollinators (Garibaldi et al., 2011). However, this pattern may also depend on the region in which crops are being cultivated, as yield of pollinator-dependent crops may be more stable in the tropics due to pollinators being mostly active all year (Souza et al., 2018; Rabeling et al., 2019). Also, the effect of pollinator dependence on yield may be more important in trees than in annual plants, as the former depend more strongly on the amount and quality of the pollination service (Knight et al., 2005; Petit and Hampe, 2006; Brittain et al., 2014).
Here, we conducted a comparative analysis of crop yield growth and its variation over a 57-year time series for more than 100 globally important crops. By applying phylogenetically explicit analyses, we assessed the influence of climatic region (i.e., tropical vs. temperate) and plant intrinsic factors (i.e., type of harvested organ, pollinator dependence, and life form) on mean annual yield growth and its variability, as well as explored possible interactions between these factors. Specifically, we predicted higher yield growth and/or yield stability in tropical/subtropical than temperate crops, in crops cultivated for their vegetative parts, in short-lived crops, and in those with reduced dependence on pollinators. Our results supported several of these expectations and revealed interesting interactions, broadening our knowledge of the ecological factors that affect crop yield growth and stability.
Data on crop yield (hectograms/hectare) were obtained from the United Nations Food and Agriculture Organization database for 113 crops and crop items (i.e., aggregations of different species; Aizen et al., 2019; Table A1) from 1961 to 2017 (FAOSTAT, 2019). Temporal series for three crops were shorter (cassava leaves, 1990–2017; kiwi, 1970–2017; triticale, 1975–2017). With these data we estimated, for each crop, the mean yield growth, Δyield, as
with t being a given year, N the total number of years with data (i.e., 57 years for most crops, starting from 1961), and the relative yield growth rate between year t and year t+1. Similarly, we estimated the variability in yield growth, SD(Δyield), as
with SD(Δyield) being the standard deviation of . This measure of variability in annual yield growth is basically a linearly detrended measure of interannual variation in (log) yield (hereafter “interannual yield variation”) and thus an inverse measure of yield stability. Also, even though Eq. (1) can be simplified as , this more complex expression reveals that Eqs. (1) and (2) depict the first (position) and second (dispersal) moments of the distribution of annual yield growth, respectively. Since both Δyield and the SD(Δyield) are based on differences in log yields, they provide comparable relative estimates of yield growth and its variation across crops, while increasing compliance of these response variables with normal-distribution assumptions underlying the linear tests used to analyze data. Also, these two measures are unitless, as the difference between log yields is the log of their ratio. In the case of mean yield growth, provides the mean annual percent increase in yield.
The crop climatic region of origin (i.e., tropical or temperate) was searched from the literature (Table A2); crops were categorized as belonging to the two main climatic regions: “tropical-subtropical” when their region of origin never exceeded 35∘ latitude and “temperate” when their region of origin extended above 35∘ (Jeffery et al., 2017). In general, tropical crops are being cultivated mainly in the tropics, while crops originating in temperate regions are being cultivated mainly in temperate zones (Leff et al., 2004). Even though some temperate crops like wheat are cultivated both in temperate and tropical latitudes, most of its production is accounted for by temperate countries (e.g., China, Russia, Ukraine, USA, Canada, Argentina). Similarly, a greater share of the global production of subtropical/tropical staple crops like maize and rice that are widely cultivated in temperate latitudes comes from tropical/subtropical countries or tropical/subtropical regions within countries (FAOSTAT, 2019). Therefore, we assume that crop climatic region of origin reflects the climatic region of cultivation. Also, for animal-pollinated crops, optimal yields are expected in the region of origin (Garibaldi et al., 2013; Brown and Cunningham, 2019). Data on type of harvested organ (i.e., vegetative or reproductive organs) and life form (i.e., herbs, shrubs, or trees) were also obtained from the literature (Milla, 2020). Pollinator dependence data for each crop were extracted from Klein et al. (2007) and Aizen et al. (2019), the latter for crops not included in the former study, where five classes were defined: “none”, for no yield reduction in the absence of pollinators; “little”, for the range 0 %–10 % of yield reduction without pollinators; “modest”, for the range 10 %–30 % of yield reduction; “considerable” for the range 40 %–90 % of yield reduction; and “essential”, for cases where yield reduction in the absence of pollinators exceeded 90 %.
A synthesis-based phylogeny (i.e., a phylogeny that is obtained by sub-setting an already available mega-phylogeny) was built to represent phylogenetic relations among crops. This kind of phylogenies has proved robust to detect even weak phylogenetic signals and to be useful in community phylogenetic analyses (Li et al., 2019). The first step to obtain the synthesis-based tree involved checking crop species names to match accepted names in The Plant List (Table A1). An initial phylogeny including all checked species was then obtained using the function “phylo.maker” from the R package V.PhyloMaker, using the GBOTB.extended mega-phylogeny (74 531 tips) as backbone, and the option “scenario 1”, which adds missing species as basal polytomies within their genera or families (Jin and Qian, 2019). Missing species were identified by comparing the focal species list with the tips in the mega-phylogeny. The phylogenetically closest taxa of these missing species were searched in the literature and were used as input information when running the function “phylo.maker”. This procedure has been shown to improve the placement of missing taxa into the resulting phylogeny (Jin and Qian, 2019).
A phylogenetic tree with 157 tips was obtained with the methodology described above. This tree was then modified to match FAO crop items (i.e., 113 items) by collapsing those nodes that included species belonging to the same FAO items. Six FAO items (i.e., “anise, badian, fennel, and coriander”, “nutmeg, mace, and cardamoms”, “mangoes, mangosteens, and guavas”, “green chilies and peppers”, “dry chilies and peppers”, and “millets”) included species phylogenetically dispersed, even belonging to unrelated families (Table A1); these items were excluded from the analyses. In some cases, FAO items comprised species phylogenetically dispersed (Table A1) but that could be represented as soft polytomies including a few items (e.g., “Brassicaceae clade”, which included the items “rapeseed”, “mustard seed”, “cauliflowers and broccoli”, and “cabbages”); these cases were kept in the analyses (see Fig. A1). The clade comprising the crops “potatoes”, “tomatoes”, and “eggplants” was resolved according to Milla (2020).
Phylogenetic signals in mean yield growth and interannual yield variation were calculated with Blomberg's K index (Blomberg et al., 2003). This index quantifies the amount of phylogenetic signal in the data relative to a Brownian motion (BM) model of trait evolution, with K=0 indicating a random distribution of the trait along the phylogeny (i.e., absence of phylogenetic signal) and K=1 reflecting a BM pattern of trait evolution (i.e., presence of phylogenetic signal). K estimates were obtained with the R package phytools (Revell, 2012), and their statistical significance was assessed by generating 10 000 randomized values of K. Furthermore, as phylogenetic signal may vary across the phylogeny, we looked for the existence of local hotspots of phylogenetic autocorrelation by estimating local indicators of phylogenetic association scores (LIPA scores hereafter) for each crop in the phylogeny (Anselin, 1995; Keck et al., 2016). Positive LIPA scores for a given trait of interest indicate that the phylogenetic neighborhood of a focus tip in the phylogeny is more similar for that trait than expected by chance. LIPA scores and their statistical significance were obtained with the R package phylosignal, on the basis of patristic phylogenetic distances and 999 randomizations (Keck et al., 2016).
Even in the absence of phylogenetic signal in the response variables, accounting for species-shared evolutionary history is recommended in interspecific comparisons (Felsenstein, 1985; Revell, 2010). Therefore, the associations of yield growth and interannual yield variation with climatic region, type of harvested organ, pollinator dependence, and life form were evaluated by conducting phylogenetic least squares (PGLS; Paradis, 2012) regressions, which account for phylogenetic non-independence among species. Phylogenetic correlations among species are made explicit in these regressions by including a residual variance–covariance matrix, which can be constructed by assuming different evolutionary models. PGLS regressions were ran using the ape v. 5.3 (Paradis and Schliep, 2019) and nlme v 3.1-140 (Pinheiro et al., 2019) R packages, and the fit of the residuals to different evolutionary models (as available in the ape R package) was compared in terms of the Akaike information criterion (AIC). Following a step-up analysis strategy (West et al., 2007), mean yield growth and interannual yield variation were regressed, alternatively, against single predictors (i.e., climatic region, type of harvested organ, pollinator dependence, or crop life form) and against combinations of two predictors to account for predictor interactions and potential confounding effects (Mazer, 1989). Higher factorial designs were not analyzed due to being too incomplete and unbalanced. Also, the tree category was excluded from the “type of harvested organ + life form” combination given that only reproductive organs (i.e., fruits or seeds) are harvested from the included tree crops. Finally, the two-predictor combination “type of harvested organ + pollinator dependence” was not tested, as the development of the vegetative organs that we consume does not depend on pollination, and thus these two factors do not cross. All predictors were treated as categorical variables in the analyses; however, the existence of a linear trend was evaluated for the relations between pollinator dependence and yield growth and yield stability given that pollinator dependence itself has an increasing (or decreasing) order across categories. In these cases, the five different categories of pollinator dependency were assigned discrete values from 0 to 4 for “none”, “little”, “modest”, “considerable”, and “essential”, respectively. Model-estimated means and their standard errors were calculated using the R package effects (Fox and Weisberg, 2019).
Mean annual yield growth was about 0.008 (equivalent to 0.802 % yr−1) and highly variable across crops, ranging from an average logarithmic increase of 0.025 (2.546 % yr−1) in kiwis to a decrease in yield of −0.037 (−3.614 % yr−1) in currants (Table A3). The most stable crop in terms of yield variation was lettuce, with an interannual variation of 0.019, followed by sugar cane and rice (0.020 and 0.022, respectively). On the contrary, the greatest interannual yield variation, 0.425, was observed in jojoba, which could relate to the quite extreme arid conditions present in the regions where it is mostly grown (Al-Obaidi et al., 2017; FAOSTAT, 2019). This crop departed clearly from the rest (about 50 % more variable than Brazil nuts, 0.291, and pistachios, 0.282, the following most variable crops; see Fig. A2), and thus it was considered as an outlier and excluded from the analyses of the determinants of yield growth stability. Mean annual yield growth and interannual yield variation were negatively, albeit weakly correlated across crops (, p<0.001). Thus, those crops with more variable yields also tended to exhibit lower yield grow rates.
Differences in crop yield growth could not be explained by crop similarity due to common ancestry, as there was no evidence of an overall phylogenetic signal in this trait (, p=0.331). Accordingly, only 6 % of all crops, mainly belonging to the Prunus clade, were surrounded by phylogenetic neighborhoods with similar yield growths (i.e., significant local positive phylogenetic autocorrelation; Fig. A3). Phylogenetically controlled regressions showed no significant effects of climatic region or type of harvested organ on the rate of yield growth (Table A4). Yield growth tended to decrease with pollinator dependence (Table A4; linear trend contrast: , SE = 0.008, p=0.047) and was about 64 % and 88 % lower in shrubs and trees than herbs, respectively (, SE = 0.003, p=0.015 for shrubs; and , SE = 0.002, p<0.001 for trees). However, a significant statistical interaction between pollinator dependence and life form (Table A4) indicated that the reduction in yield growth associated with pollinator dependence is only evident in tree crops (Fig. 1; linear contrasts with β=0.005, SE = 0.011, p=0.642 for herbs; β=0.028, SE = 0.023, p=0.225 for shrubs; and , SE = 0.013, p=0.006 for trees). Therefore, tree crops that are highly dependent on pollinators showed, on average, the lowest growth in yield.
Crop similarity due to common ancestry was not reflected in yield stability, as there was no evidence of phylogenetic signal in interannual yield variation globally (, p=0.651). Local phylogenetic autocorrelation was detected but involved only ca. 10 % of all crops, with significant LIPA positive scores detected in all members of the [Amaryllidaceae + Asparagaceae] clade as well as in other six phylogenetically dispersed crops (Fig. A3). Interannual yield variation was 33 % higher in temperate than tropical crops (β=0.027, SE = 0.011, p=0.020; Fig. 2a) and 65 % higher in those crops cultivated for consumption of their reproductive organs than in crops cultivated for their vegetative organs (β=0.039, SE = 0.015, p=0.010; Fig. 2b). These results were not confounded by the inclusion of tree crops that are only harvested for their seeds or fruits, as a significant difference in yield variability persisted after excluding trees and controlling for the remaining growth forms (Table A4; Fig. A4). Interannual yield variation tended to increase with increasing pollinator dependence (Fig. 2c; linear contrast: β=0.105, SE = 0.048, p=0.032), despite the overall test not being statistically significant (Table A4). Crops highly dependent on animal pollination were, on average, about 50 % more variable in yield that those that do not depend, or depend little, on pollinators. Finally, interannual yield variation was 37 % higher in trees than in herbaceous crops (β=0.030, SE = 0.013, p=0.023), with shrubs showing values of yield variability closer to trees than to herbs (Fig. 2d).
Increasing crop yield to fulfill the continuous rising food demands from a growing human population, while minimizing the impact on natural ecosystems, is one the main challenges of modern agriculture (Tilman, 1999; Tilman et al., 2002; Foley et al., 2011; Bommarco et al., 2013). Genetic and management innovations have boosted a steady increase in crop yield since the middle of the last century (Evenson and Gollin, 2003; Garibaldi et al., 2011; Hatfield and Walthall, 2015). However, the first signs of yield deceleration and stagnation have already been reported for some globally important crops (Ray et al., 2012; Kucharik et al., 2020). Under this scenario, an ecological perspective can be crucial to broaden our knowledge of the factors affecting crop yield growth. By applying a comparative approach, here we uncovered the influence of environmental and plant intrinsic traits on average yield growth and on its interannual variation. Specifically, we found that yield growth decreased with increasing pollinator dependence in tree crops but not in herbaceous and shrubby crops. Interannual yield variation was higher in crops from temperate regions, in those cultivated for their reproductive organs, and in tree and shrubby crops as compared with herbaceous ones, and it tended to increase with increasing pollinator dependence. Unexpectedly, average yield growth and its variation were not phylogenetically structured. Therefore, our results revealed new and intriguing patterns, which we discuss below.
There was no evidence that climatic region was related to yield growth, with temperate crops exhibiting similar mean growth rates to tropical-subtropical crops (0.72 % yr−1 vs. 0.83 % yr−1). Under the assumption that the climatic region where a crop (or its ancestors) originated reflects the climatic conditions where the crop is most commonly cultivated, higher temperature and an overall more benign environment for plant growth in the tropics was not reflected in significantly higher rates of yield growth. As proposed in the Introduction, it might well be that more intense weed competition and, perhaps, higher herbivore pressure at low latitudes counteract the positive effect of a more benign and stable climate on crop development (Rosenzweig and Liverman, 1992). Alternatively, crop genetic and management improvements could have been more prevalent and intense among temperate crops (e.g., wheat, canola). However, this seems unlikely as several tropical-subtropical crops have also been genetically manipulated intensively and are grown industrially (e.g., soybean, rice, maize; Aizen et al., 2019). Despite no apparent differences in yield growth, we did find that interannual yield variation was lower in tropical-subtropical than temperate crops, probably reflecting higher climatic stability at lower latitudes. Previous studies focusing in four of the most economically important crops (i.e., wheat, maize, soybean, and rice) have identified temperature and precipitation variability as the main factors explaining yield variation (Ray et al., 2015; Schauberger et al., 2016). While water availability may limit plant growth in both zones (Kramer, 2019), temperature amplitude is greater in temperate zones, and occasional extreme temperatures may occur more frequently in these zones (e.g., occurrence of frosts; Rodrigo, 2000; Snyder and de Melo-Abreu, 2005). The stability and performance of many physiological and biochemical processes affecting plant growth – including photosynthesis, stomatal conductance, and nutrient uptake – depend on an optimal temperature range and can be disturbed by the occurrence of temperatures outside this range (Schauberger et al., 2016; Slot and Winter, 2017). Given that the greater yield variability observed among temperate crops was independent of whether the crops were harvested for their vegetative or reproductive organs (Table A4), higher yield variation in temperate regions may be explained by extreme temperatures affecting biochemical processes involved in the development of both vegetative and reproductive organs.
Yield growth seems to be independent of whether a crop is cultivated for its vegetative or for its reproductive parts. However, crops cultivated for their vegetative parts show more stable yields than those cultivated for either their fruits or seeds. This lower variation may result from the fact that investment in vegetative parts (i.e., leaves, stems, roots, tubers, rhizomes) is quintessential to plant survivorship, and even though it can be regulated, it cannot be postponed (Horvitz and Schemske, 2002; Obeso, 2002). On the contrary, variable resource availability can determine high variability in fruit and seed production among reproductive seasons in iteroparous species (Weiner et al., 2009; Hulshof et al., 2012), and even in annual plants, in which sexual reproduction in a given year can fail entirely (Kho, 2000). Besides resource availability as an intrinsic source of variability, most fruit and seed crops depend to different degrees on an external agent, either wind or insect pollinators, for pollen transfer between flowers (Klein et al., 2007). Particularly, restricted pollen transfer due to pollinator scarcity can be an important factor limiting fruit and seed set in a large fraction of wild plants and crops. In fact, pollen limitation (i.e., the failure of achieving maximum seed set as a consequence of inadequate pollination; Knight et al., 2005) affects more than a half of all crops (Aizen et al., 2008). As a consequence, pollinator availability, which is highly variable in time and space (Herrera, 1988; Price et al., 2005), can also determine high variability in yield. Agreeing with this hypothesis, we report a trend of increasing interannual yield variation with increasing dependence on animal pollination. This confirms results from previous reports (Garibaldi et al., 2011), although our conservative analysis controlled for phylogenetic non-independence among crops.
Pollen limitation has also been proposed to limit yield growth in addition to decreasing yield stability. In fact, a proposed global pollinator decline is expected to affect total agriculture production by decelerating yield growth or even decreasing the yield of pollinator-dependent crops (Aizen et al., 2008; Potts et al., 2010). Even though previous studies have reported that yield growth decreased with increasing crop pollinator dependence (Aizen et al., 2008; Garibaldi et al., 2009, 2011), these studies did not account for potentially confounding factors and phylogenetic non-independence. In particular, by accounting for growth form, we found that this trend was only apparent in trees, in which high pollinator dependence seems to hinder yield growth. In fact, several tropical-subtropical and temperate tree crops that depend to a large extent on pollinators to produce either fruits or seeds, or even fail to produce fruits or seeds without pollinators, have shown negative growth rates during the last decades (e.g., Brazil nuts, kola nuts, cashew, plums, cherries, quinces, blueberries; Table A3), supporting the view that a global pollinator decline is affecting crop yield. However, it is puzzling that no trend for decreasing yield was observed among herbaceous crops, and apparently a concave trend was found for shrubs (Fig. 1). Several factors could explain these discrepancies. First, independent of their pollinator dependence, there seems to be lower pollen limitation in herbaceous than woody plants (Knight, 2005). Therefore, and perhaps associated with much larger floral displays and higher incidence of self-incompatibility, greater pollinator abundance is needed to maximize crop yield in trees than in herbaceous crops (Garibaldi et al., 2020). Second, hand and other forms of artificial pollination constitute a customary procedure in highly valuable herbaceous and shrubby crops like vanilla and kiwi, respectively (Arditti et al., 2009, Sáez et al., 2019), which lowers their dependence on declining insect pollinators. Although there are some accounts of fruit production based on hand pollination for highly pollinator dependent tree crops (e.g., apples in China; Partap et al., 2001; Partap and Ya, 2012), this is a highly laborious and geographically restricted procedure.
It has been proposed that reduced yield growth could be a consequence of higher variability of a crop's input resource (i.e., pollinators) via what is known as Jensen's inequality (Jensen, 1906; Ruel and Ayres, 1999), which is predicted when there is a positive but saturating response of yield with an increase in an agriculture input (Garibaldi et al., 2011). In this case, variability in an agriculture input resource is expected to be reflected in higher yield variation, resulting in a decrease in average yield over years. In fact, higher variability in yield associated with larger reproductive uncertainty has been proposed as an explanation of reduced yield in highly pollinator dependent crops (Garibaldi et al., 2011). Although here we report an overall negative relation between yield growth and variability, as expected due to Jensen's inequality, the interactive effects of growth form and pollinator dependence on yield growth still persisted after accounting for yield variation (Table A5). Thus, reduced yield growth in highly pollinator dependent trees can be interpreted as a direct consequence of their dependence on this external biotic input rather than of the yield uncertainty introduced by this dependence.
Lower pollen limitation in herbaceous than woody plants might also explain why in general yield growth and yield stability decreased along a gradient of crop increasing woodiness. Moreover, herbs and trees differ in the length of their life cycles, which influences the pattern of resource allocation between vegetative and reproductive structures. Life cycles are shorter in herbs, and resources are invested mainly in vegetative growth and reproduction. Trees have longer life cycles, they grow taller, and have higher costs of maintenance as resources are needed for the development of supportive and protective tissues, which reduces growth rates (Petit and Hampe, 2006). Furthermore, woody species are often characterized by a variable and synchronized reproductive behavior known as “masting”, which may increase plant fitness by increasing either pollination success, seed dispersal, or offspring survival through predator satiation (Pearse et al., 2016). This reproductive strategy, although beneficial for wild plant populations, is highly undesirable in agriculture, as it can increase interannual yield variation and price peaks (Smith and Samach, 2013; Ray et al., 2015). All tree crops included in this study are being cultivated for exploitation of their fruits or seeds, and their interannual variation in yield may reflect, in addition to higher pollination limitation, yearly fluctuations in resources invested in reproduction.
Finally, it is interesting that neither mean yield growth nor its variation were conditioned by crop common ancestry in the majority of the analyzed crops. This is a meaningful finding that indicates that crop genetic and management improvements could overcome several developmental and ecological conditionings, besides those analyzed here, which may be phylogenetically structured. As a consequence, phylogenetically related crops that probably have been manipulated genetically to different extents can exhibit contrasting yield growth rates (e.g., apples vs. quinces; Table A3).
The strength of a comparative approach lies in revealing general patterns. This approach has been rarely applied in inter-specific studies of crop yield, despite the need for identifying global factors limiting crop yield growth and yield stability. This is of paramount importance in a context of decelerating yield growth and increasing yield variability expected under climate change (Chalinor et al., 2014, Zhao et al., 2017) and global pollinator decline (Aizen et al., 2008; Potts et al., 2010). By analyzing yield growth and interannual yield variation of more than 100 globally important crops, here we identified ecological factors associated with climate, resource allocation, and pollination limitation that affect crop yield. Despite the ultimate processes and mechanisms underlying these patterns, the ecological correlates of yield growth and yield variation detected here provide a useful starting point for establishing management guidelines for crop selection. For instance, even though pollinator-dependent tree crops have relatively high market values (Bauer and Wing, 2016), agronomic schemes based solely on the cultivation of this type of crops is a risky business because of their reduced yield growth and high interannual variability, particularly in temperate regions. In any event, the relative reduced yield growth and high yield variability of highly pollinator dependent tree crops (i.e., those in the moderate and essential categories) call for the need to apply a more active and knowledge-based pollinator management than is commonly performed today. This requires not only the management of domesticated pollinators (e.g., Apis mellifera), but also the enhancement of wild pollinators through infield and outfield strategies that involve habitat management at different spatial scales (Garibaldi et al., 2014). On the other hand, agronomic schemes based exclusively on crops cultivated for either their vegetative parts or with low levels of pollinator dependence could show adequate levels of yield growth and stability, but their production is of a poorer nutritional quality and has lower market prices than the one represented by the seeds and fruits of many pollinator-dependent crops (Gallai et al., 2009; Eilers et al., 2011). Overall, our results advocate for more diverse agriculture that involves the cultivation of different crops with different ecological features, nutritional quality, and market value at all spatial scales. In addition to contributing to increasing food security in quantitative and qualitative terms, this more diversified agriculture will ensure a more sustainable agriculture and the preservation of different ecosystem services (Aizen et al., 2019).
The data used in this study can be obtained from sources cited in the main text and also from Appendix A.
GG and MAA conceived the study and designed the methodology; GG analyzed the data; GG and MAA wrote the original manuscript; AS, GG, NLdC, and MAA contributed substantially to the final manuscript.
The authors declare that they have no conflict of interest.
The authors thank Rubén Milla for providing very helpful comments on a previous version of this paper and acknowledge the support of the SURPASS2 project funded under the Newton Fund Latin America Biodiversity Programme: Biodiversity – Ecosystem services for sustainable development grants awarded by the Natural Environment Research Council of Great Britain (NERC; grant no. NE/S011870/1), the National Scientific and Technical Research Council of Argentina (CONICET; grant no. RD 1984/19), and the National Fund for Scientific and Technological Research of Argentina (FONCYT; grant nos. PICT 2015-2333, PICT 2018-2145, and PICT-2018-03559).
This paper was edited by Daniel Montesinos and reviewed by Rubén Milla and one anonymous referee.
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