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Annals of Botany logoLink to Annals of Botany
. 2020 Apr 25;126(5):825–835. doi: 10.1093/aob/mcaa083

How plant allometry influences bud phenology and fruit yield in two Vaccinium species

Marie-Pier Fournier 1, Maxime C Paré 1, Valentina Buttò 1, Sylvain Delagrange 2, Jean Lafond 3, Annie Deslauriers 1,
PMCID: PMC7750960  PMID: 32333756

Abstract

Background and Aims

Understanding how plant allometry, plant architecture and phenology contribute to fruit production can identify those plant traits that maximize fruit yield. In this study, we compared these variables and fruit yield for two shrub species, Vaccinium angustifolium and Vaccinium myrtilloides, to test the hypothesis that phenology is linked to the plants’ allometric traits, which are predictors of fruit production.

Methods

We measured leaf and flower phenology and the above-ground biomass of both Vaccinium species in a commercial wild lowbush blueberry field (Quebec, Canada) over a 2-year crop cycle; 1 year of pruning followed by 1 year of harvest. Leaf and flower phenology were measured, and the allometric traits of shoots and buds were monitored over the crop cycle. We hand-collected the fruits of each plant to determine fruit attributes and biomass.

Key Results

During the harvesting year, the leafing and flowering of V. angustifolium occurred earlier than that of V. myrtilloides. This difference was related to the allometric characteristics of the buds due to differences in carbon partitioning by the plants during the pruning year. Through structural equation modelling, we identified that the earlier leafing in V. angustifolium was related to a lower leaf bud number, while earlier flowering was linked to a lower number of flowers per bud. Despite differences in reproductive allometric traits, vegetative biomass still determined reproductive biomass in a log–log scale model.

Conclusions

Growing buds are competing sinks for non-structural carbohydrates. Their differences in both number and characteristics (e.g. number of flowers per bud) influence levels of fruit production and explain some of the phenological differences observed between the two Vaccinium species. For similar above-ground biomass, both Vaccinium species had similar reproductive outputs in terms of fruit biomass, despite differences in reproductive traits such as fruit size and number.

Keywords: Carbon allocation, plant allometry, phenology, plant architecture, fruit production, plant biomass, Vaccinium angustifolium, Vaccinium myrtilloides

INTRODUCTION

How a plant allocates carbon for reproduction is fundamental to explaining fruit yields. The allometry of biomass partitioning – the differential growth of plant parts (Aarssen, 2008) – and the trade-off between vegetative and reproductive growth are at the base of life strategies of plants and are species-specific. Carbohydrates produced via photosynthesis are allocated to metabolism, growth of above- or below-ground structures, formation of reserves, and reproduction (Körner, 2003; Park et al., 2009; Hartmann and Trumbore, 2016); thus, plants partition carbon among different growing structures. Reproductive biomass – fruit yield in commercial species – matches plant biomass (Weiner et al., 2009) and allometry of leaf traits (Chang et al., 2017). These characteristics reflect both potential energy and the photosynthetic capacity for reproduction. In commercial blueberries (Vaccinium sp.) where fruit yield is important, excess available carbohydrates are first allocated to reproduction and then to vegetative growth (Swain and Darnell, 2001; Chang et al., 2017).

A better understanding of plant phenology – the developmental stages of plant parts in time (Badeck et al., 2004) – physiology and architecture, i.e. the organization of the different plant parts (Barthélémy and Caraglio, 2007), is necessary to provide information on how to maximize fruit yields. The meristems, represented by both vegetative (i.e. growth) and reproductive buds, form a population of functional units or elements that compete for resources (Bonser and Aarssen, 2003). As resource allocation is allometric in a broad sense (Weiner, 2004), resource partitioning within plants can differ depending on the number of elements (size-dependent effect) influencing phenology (Mason et al., 2014; Barbier et al., 2015), growth and reproductive outputs (Bonser and Aarssen, 2003). For example, flower bud abundance, leaf surface area and plant biomass are three plant traits that can affect fruit production; however, their relative importance can be altered through agricultural practices (Yarborough, 2004, 2012).

In commercial wild blueberry fields, crop management consists of a 2-year crop cycle. The cycle begins with mechanical pruning in late autumn, about 2 months after fruit harvesting. The following growing season – the pruning year – is used for vegetative growth where shoot development occurs from rhizomes to produce both leaf and flower buds for the second year. During the second year – the harvesting year – both fruit production and fruit harvesting occur (Chiasson and Agrall, 1996). In the pruning year, new shoot growth is driven by the translocation of root carbohydrates that supply carbon and nutrients to the vegetative buds (Loescher et al., 1990; Morin, 2008; Kaur et al., 2012). In the harvesting year, however, carbon allocation is controlled mainly by the abundance and type of buds (Gauci et al., 2009; Kaur et al., 2012), as well as fruit characteristics (Li et al., 2015). Depending on the strength of the carbon sink, a trait that varies between species, vegetative growth can be slowed, sped up or delayed (Kaur et al., 2012). Species allometry and phenology modify the presence and abundance of fruit as the number of reproductive units, such as flowering buds, alters patterns of carbon allocation and partitioning (Lacointe, 2000; Marcelis and Heuvelink, 2007).

Earlier phenology is precarious in northern regions for the two Vaccinium species studied here because of the possibility of spring frosts, the main factor reducing wild blueberry fruit yield (Olson and Eaton, 2001; Strik and Yarborough, 2005; Ministère de l’Agriculture, 2016). Although some commercial blueberries, such as Vaccinium angustifolium and Vaccinium myrtilloides, demonstrate cold hardiness and adaptation, temperatures below −2 °C during flower bloom can seriously injure reproductive structures and reduce fruit development and yield (Olson and Eaton, 2001; Yarborough, 2015). The timing of plant phenology is determined by both the genetic characteristics of species and the local climate (Badeck et al., 2004; Bell, 2009; Anna and Rufus, 2012). This leads to earlier or later phenological events in leaves or flowers that can influence a plant’s susceptibility to frost (Smith, 1969; Lin and Pliszka, 2003; Hancock, 2008) and thus affect fruit yield.

In this study, we investigated the phenological and allometric characteristics of two wild lowbush blueberry species, V. angustifolium and V. myrtilloides, grown in commercial fields in the Lac-Saint-Jean region of Quebec, Canada. We aimed to understand how these phenological and allometric traits influence fruit yield. Specifically, we tested the hypotheses that (1) leaf and flower phenology are linked to the plants’ allometric traits and species; and (2) both phenology and plant allometry are predictors of fruit production.

MATERIALS AND METHODS

Experimental design

We conducted our study from spring 2017 to autumn 2018 at the Bleuetière d’Enseignement et de Recherche (BER) in Normandin Quebec, Canada (48°49′35ʺN, 72°39′35ʺW). We established an experimental design that included two adjacent sites composed of two fields at each site and four blocks of 12 experimental units (EUs) in each field arranged in a split-plot design (Supplementary Data Fig. S1). Each site contained 96 EUs, each 15 × 22 m (330 m2), separated by 3-m buffer zones. All EUs received one of 12 different treatments. These treatments were combinations of mechanical or mechanical and thermal pruning, with or without fungicide application, and mineral, organic or without fertilization (Table S1, Fig. S1). However, the effects of these various treatments are not presented in this paper, but see Fournier (2020). Site 1 was pruned thermally in autumn 2016 and mechanically in spring 2017. Site 1 was harvested in 2018. Site 2 was pruned mechanically and thermally in autumn 2017. Site 2 was in a pruning year in 2018 and a harvesting year in 2019 (after completion of this study). In addition, 52 beehives were used in spring 2018 to ensure sufficient flower pollination during the harvesting year (Table S1).

Data collection

Immediately before the beginning of the growing season, eight shoots per EU were selected at random. As we wished to record early phenological changes, our initial measurements were recorded on shoots. We based our selection criteria on the observation of a primary leaf bud having reached Stage 1 to avoid buds showing no development (Supplementary Data Figs S2 and S3). The same eight shoots in each EU were then monitored periodically throughout the growing season, for phenological measurements. We noted the species Vaccinium angustifolium Aiton (VA) or Vaccinium myrtilloides Michx (VM) when we observed and measured plant characteristics. In total, we monitored 604 plants of V. angustifolium and 164 plants of V. myrtilloides during the Site 1 pruning year (2017). During the Site 1 harvesting year (2018), we monitored 606 and 162 plants of V. angustifolium and V. myrtilloides, respectively. During the pruning year of Site 2 (2018), we monitored 585 V. angustifolium and 183 V. myrtilloides plants. We recorded leaf bud phenology over the pruning and harvesting years at both sites using the same shoot, with measurements every 3–4 d (Table S1) following a six-stage leaf development protocol (Figs S3 and S4). Floral and fruit bud phenology were also recorded for Site 1 (every 3–4 d) during the harvesting year using an 11-stage development protocol (Figs S5 and S6).

We recorded several allometric traits of the blueberry shoots (Supplementary Data Fig. S2). In pruning years, we noted the number (nb) of leaves and ramifications and plant height (cm). In the harvesting year (only Site 1), we recorded the number of leaf buds, flower buds, apical and total flowers, leaves, branches and ramifications, plant height (cm), and branch length (mm). We measured these characteristics when they had attained their maximum values; thus, we noted these values once during the growing season. We then hand-harvested the fruit of each monitored plant to determine the number of fruits – apical and total number – and fruit biomass (BM) [g of fresh biomass (FM)] (Fig. S2). At the end of the harvesting year, a quarter of the monitored plants in Site 1 were cropped (192 plants in total; 145 V. angustifolium and 47 V. myrtilloides) to collect and determine leaf BM [g of dry biomass (DM)] and leaf area (cm2) as well as the above-ground plant BM (g DM), excluding fruits (Fig. S2). Leaf area (cm2) was measured with a planimeter (Li-3100, Li-Cor, Lincoln, NE, USA). Based on these collected data, above-ground plant BM, leaf BM and the measured leaf area were extrapolated for all plants at both sites (n = 1534) using regressions of plant leaf number and height (Tables SM1–2 and Fig. SM1). We calculated specific leaf area (SLA) as:

SLA (m2kg)=leaf area (cm2)dry leaf mass (mg)100

Meteorological data

We installed a meteorological station inside the experimental design to record meteorological data, such as temperature (°C) and precipitation (mm), at 5-min intervals. Table 1 presents the meteorological data for both years of our study.

Table 1.

Mean monthly minimum, mean and maximum temperature and total monthly rainfall (mm) for May–August for the two years (2017–2018) of the study.

Month (DOY) Temperature (°C) Total rain (mm)
Minimum Mean Maximum
2017
May (121–151) 5.53 ± 3.50 12.90 ± 2.62 19.82 ± 3.92 16.6
June (152–181) 8.37 ± 3.98 15.87 ± 3.63 22.40 ± 4.52 115.4
July (182–212) 9.06 ± 4.06 17.51 ± 2.60 24.82 ± 3.10 72.6
August (213–243) 9.31 ± 3.45 15.62 ± 2.39 21.98 ± 3.40 123.6
2018
May (121–151) -0.13 ± 5.10 9.26 ± 5.24 17.57 ± 7.26 41.4
June (152–181) 6.60 ± 4.67 15.73 ± 4.44 23.00 ± 5.68 36.6
July (182–212) 15.66 ± 4.57 21.45 ± 2.70 28.30 ± 3.47 26.4
August (213–243) 12.92 ± 2.81 20.04 ± 2.17 27.08 ± 1.90 75

Statistical analysis

We assessed leaf and floral bud phenology as qualitative ordinal variables. The stages were expressed by their frequency for each sampling day, expressed as day of the year (DOY) (Deslauriers et al., 2019). We calculated the average date (x¯), standard deviation (sx¯), and standard error of the mean (sex¯) at which the Ei stage occurred using:

x¯=i=1kfEi×xin,
sx¯=i=1k(xix¯)2n1,
sex¯=sx¯n,

where xi is the date expressed in DOY, fEi is the frequency of the Ei stage and k is the number of sampling dates, as adapted from Scherrer (2007).

We developed a generalized multinominal logistic model to compare bud phenology between species (GENLINMIXED procedure in SPSS Statistics). The input data for the generalized multinominal logistic model was a frequency table where the Ei stage was expressed by its frequency of observation for each sampling day (DOY). In the model, species, year and the date at which the Ei stage occurred were fixed variables, while fields, blocks (nested in fields) and EU (nested in fields, blocks and species) were run as random variables. We used the LINK option of LOGIT (SPSS Statistic) for the linkage function between the probabilities of the phenological response – linked to DOY – and fixed variables. This procedure produces logistic regressions, also known as logit probability models, where the explanatory variable, phenological stage, is a qualitative ordinal variable. The covariance structure in the RANDOM argument was determined as autoregressive (AR1) by the COVTYPE option (GENLINMIXED procedure in SPSS Statistic). The produced main logit probability model then determined the differences between species for both the leaf and productive buds; flowers and fruit were in the same logistic model. The probability P(Ei), which represents the probability of observing a phenological stage Ei at a given DOY x, was calculated separately by species using the estimate Est. Est is the sum of all fixed model coefficients (b) included for a specific combination, such as stage (bEi), species (s) and, if applicable, year (y), giving:

Est=(bEi+bs+by)

Also, P(bEi) represents the DOY when there is a 50 % probability of passing through stage Ei; thus, P(50) is similar, but it includes the effects of species and, if applicable, year. Those elements were calculated from:

P(bEi)=bEibDOY
P(50)=EstbDOY+2P(bEi)

Generalized linear mixed models were performed using IBM SPSS Statistics 25 (IBM Corp., 2017.

We used structural equation modelling (SEM) to assess the direct and indirect effects of bud allometric traits on phenology and fruit number and biomass for both V. angustifolium and V. myrtilloides. The model structure was established based on our hypothesis, according to which the number of units (leaf and flower bud elements) influence bud phenology (Fig. 1). Plant productivity is thus influenced by both the number of units and bud phenology. Only P(50), representing the DOY for passing from Stage 5 to Stage 6, was included in the SEM because it represents the DOY at which the phenology was completed for both leaf and flower buds. The degree of multicollinearity between variables was assessed by variance inflation factors (VIFs), retaining all variables having a VIF value <5 (Zuur et al., 2010). SEM analysis was run using the lavaan package in R (Rosseel, 2012), with 1000 bootstrap resampling (Beaujean, 2014). The model was accepted when Pχ2 > 0.05, and goodness of fit was assessed using the fitting index combination of a comparative fit index (CFI) of >0.95 and a standardized root mean square residual (SRMR) of <0.09 (Hooper et al., 2008).

Fig. 1.

Fig. 1.

Conceptual model of the relationship between the number of units of leaves and flower buds, their phenology, and fruit production.

Using the PROC MIXED procedure in SAS, we developed linear mixed models to compare the two species in terms of the measured variables and allometric traits, as illustrated in Supplementary Data Fig. S2 (except for phenology). We used species and year (if applicable) as fixed factors, and blocks (nested in fields) and EU (nested in blocks, fields and species) as random factors.

We used linear regressions, as described by Weiner et al. (2009), to fit the R–V model for both V. angustifolium and V. myrtilloides, using reproductive biomass (R or fruit BM) as the dependent variable and vegetative biomass (V or above-ground plant BM) as the independent variable. The two variables were log10-transformed to improve normality. A mixed-effect model linked the two variables and species. Random effects included fields, blocks (nested in fields) and EU (nested in blocks, fields and species). Mixed-effect models were built using a backward process (PROC MIXED procedure in SAS), where non-significant (P > 0.05) factors were removed from the models. The normality of the residual predicted values was verified. All linear mixed models and mixed-effect models were developed using SAS 9.2 (SAS Institute, Cary, NC, USA).

RESULTS

Phenological differences between species

The leaf, flower, and fruit phenology of V. angustifolium and V. myrtilloides were monitored in 2017 and 2018 (Supplementary Data Figs S3–S6). During the pruning year, V. angustifolium and V. myrtilloides showed no differences in leaf phenology (Tables 2 and 3; Fig. 2A, B): the timing of the phenological phases (P(50)) of the leaves between species differed by only 1–2 d, a non-significant difference (Table 3; Fig. 2A, B). Year also had a significant effect as the overall timing of leaf phenology began at the same time in both species; however in 2017, leaf bud development finished earlier in both species by about 8 d compared to 2018 (Tables 2 and 3; Fig. 2A, B).

Table 2.

Generalized linear mixed models and pairwise tests of the effect of species and year on bud phenology. The results include the F-statistic, degrees of freedom (dfnom, dfdenom), and P-value (P): Fdf1, df2 (P). The significance of P-values is based on α = 0.05; P-values in bold are significant in the main model.

Crop cycle Type of bud Effect F df1, df2 (P)
Pruning Leaf Model 1201.8274, 8573 (P < 0.001)
Species 3.3031, 8573 (P = 0.069)
Year 223.7491, 8573  (P < 0.001)
Species × Year 1.4941, 8573 (P = 0.222)
DOY 4790.7091, 8573 (P < 0.001)
Harvesting Leaf Model 2304.7412, 6425 (P < 0.001)
Species 249.4902, 6425 (P < 0.001)
DOY 4599.9251, 6425 (P < 0.001)
Flower Model 4808.4302, 10402 (P < 0.001)
Species 173.7251, 10402 (P < 0.001)
DOY 9610.8031, 10402 (P < 0.001)

Table 3.

Day of the year (DOY) corresponding to the 50 % probability (P(50)) of reaching the following stage for leaf (L) or flower (F) buds of Vaccinium angustifolium and V. myrtilloides in the pruning years of 2017 (Pr17) and 2018 (Pr18) or the harvesting year (Hy).

Stage V. angustifolium V. myrtilloides
L – Pr17 L – Pr18 L – Hy F – Hy L – Pr17 L – Pr18 L – Hy F – Hy
0 132 126 142 134
1 146 154 139 134 147 155 150 142
2 153 161 148 146 154 162 158 154
3 158 167 152 152 160 167 162 160
4 162 170 155 157 163 171 165 165
5 166 174 158 163 167 174 169 171
6 172 179
7 181 188
8 189 196
9 203 211
10 213 220

Fig. 2.

Fig. 2.

Mean timing of the phenological stages of Vaccinium angustifolium and V. myrtilloides leaf buds in the vegetative years and the mean timing of the leaf, flower and fruit buds in the pruning and harvesting years. Error bars represent the standard error of the mean.

Phenological differences between the two blueberry species during the harvesting year were greater; relative to V. myrtilloides, the timing of leaf and flower phenology for V. angustifolium occurred about 10 and 8 d earlier, respectively (Fig. 2D, E; Tables 2 and 3). We observed significant phenological differences between species in the harvesting year for leaf bud and flower bud (Table 2). Flowering occurred later than leaf bud burst even though we observed increases in the size and swelling of the flower buds earlier than those for the leaf buds (Stage 1 for both leaf and flower buds). Leaf buds opened 5 d prior to flower buds in V. angustifolium and 2 d before flower buds in V. myrtilloides (Table 3; Fig. 2D, E). We modelled a difference of 8 d between the two species for the probability of open flowers (Stage 6, Supplementary Data Fig. S5); we observed open flowers on DOY 171 for V. angustifolium and DOY 179 for V. myrtilloides (Table 3). This delay is important given that V. angustifolium flowers were open at that time (DOY 171) while V. myrtilloides flowers remained closed (Stage 5, Fig. S5; Table 3), thereby limiting cross-pollination between the two species.

The observed earlier flower bud phenology in V. angustifolium was maintained for most of the fruit developmental stages (Fig. 2C); however, the date at which we observed the first mature fruit was similar between the species (Fig. 2C): about half of the V. myrtilloides plants had reached the last stage of fruiting when 80 % of the V. angustifolium plants had attained the same stage. This indicates a faster fruit maturation toward the end of fruit development in V. myrtilloides.

Species effect on allometric characteristics

The two blueberry species differed in most of their plant allometric characteristics, particularly during the harvesting year (Fig. 3; Table 4). During the pruning years, both species had similar plant heights (Fig. 3A), ramification numbers, plant BM (Fig. 3D), and SLA (Fig. 3J; Table 4). In the pruning years, however, we observed significantly higher leaf numbers for V. myrtilloides than for V. angustifolium (Fig. 3H; Table 4). Furthermore, we also observed a significant difference between years for leaf number (Table 4) and SLA (Table 4) in the pruning years, with both traits lower in 2018. We observed no significant year and species interactions (Table 4).

Fig. 3.

Fig. 3.

Mean of the allometric traits per plant of the two Vaccinium species. Traits are presented for the different organs: plant, leaf, flower and fruit. Data were collected in the pruning year (Pr), harvesting year (Hy) or both (All). Error bars represent the standard error of the mean. VA = V. angustifolium, VM = V. myrtilloides, nb = number, BM = biomass, DM = dry BM, and FM = fresh BM.

Table 4.

Mixed model testing of the effect of species and years on allometric traits. The results include the F-statistic, degrees of freedom of the numerator (df1) and denominator (df2), and the P-value (P > F). The significance of the P-value is based on α = 0.05; values in bold are significant in the main model. Probability (P) is not significant (n.s.) when P > 0.05 while the other degrees of significance correspond to P < 0.001 (***), P < 0.01 (**) and P < 0.05 (*). BM = biomass, SLA = specific leaf area, nb = number, abov. = above-ground.

Organ Traits Type of year
Pruning Harvesting
Effect Species Year Species × Year Species
Plant Plant abov. BM 2.541, 459 (n.s.) 0.521, 459 (n.s.) 0.021, 459 (n.s.) 3.461, 243 (n.s.)
Plant height 3.251, 445 (n.s.) 0.701, 445 (n.s.) 0.001, 445 (n.s.) 5.31 1, 235  (*)
Branch length 0.551, 277 (n.s.)
Branch nb 7.70 1, 104  (**)
Ramification nb 1.381, 410 (n.s.) 0.441, 128 (n.s.) 0.201, 403 (n.s.) 0.841, 285 (n.s.)
Leaf Leaf bud nb 24.52 1, 225  (***)
Leaf nb 7.91 1, 440  (**) 88.26 1, 92.4  (***) 1.951, 435 (n.s.) 15.40 1, 255  (***)
SLA 1.421, 562 (n.s.) 44.74 1, 181  (***) 0.261, 553 (n.s.) 0.011, 760 (n.s.)
Flower Flower bud nb 6.42 1, 304  (*)
Apical flower nb 55.27 1, 188  (***)
Total flower nb 7.54 1, 266  (**)
Flowers per bud 33.59 1, 184  (***)
Fruit Apical fruit nb 61.28 1, 228  (***)
Total fruit nb 21.76 1, 293  (***)
Fruit BM 2.561, 281 (n.s.)
BM per fruit 15.85 1, 481 (***)

During the harvesting year, plant BM (Fig. 3E), branch length (Fig. 3C), ramification numbers, SLA (Fig. 3J) and fruit BM (Fig. 3O) did not differ between the two species (Table 4). All other characteristics differed significantly between the two blueberry species; for example, V. angustifolium had a greater flower bud number (Fig. 3K) and BM per fruit (Fig. 3R) than V. myrtilloides. All other allometric traits had higher values for V. myrtilloides (Table 4), including plant height (Fig. 3B) and the number of leaf buds (Fig. 3F), leaves (Fig. 3I), branches (Fig. 3E), apical flowers (Fig. 3M), total flowers (Fig. 3L), flowers by bud (Fig. 3N), apical fruits (Fig. 3Q) and total fruits (Fig. 3P). Branch growth slowed around DOY 185, as fruits began to develop.

Links between species, phenology and allometric characteristics in the harvesting year

The SEM suitably fit our hypothesis (Pχ2 = 0.35, CFI = 1, SRMR = 0.003), underlining the direct and indirect relationships between the units’ number, phenology and fruit production. The SEM explained 70 % and 50 % of the variance in fruit biomass and total fruit number, respectively. All significant coefficients are represented in Fig. 4, while a complete list of all obtained coefficients is shown in Supplementary Data Table S2. Fruit biomass was linked positively and directly to total fruit number (0.78) and negatively, but directly, to flower P(50) (−0.08, Fig. 4). Total fruit number was affected positively by total flower number (0.7) and leaf P(50) (0.10, Fig. 4). Leaf P(50) (R2 = 0.04) covaried strongly with flower P(50) (0.67), but it was also linked directly to the number of flowers per bud (0.15) and leaf bud number (0.13, Fig. 4). Flower P(50) (R2 = 0.07) was affected positively by leaf bud number (0.19) and the number of flowers per bud (0.16, Fig. 4) but was affected negatively by total flower number (−0.26).

Fig. 4.

Fig. 4.

Structural equation model fit for both Vaccinium myrtilloides and V. angustifolium with significant standardized coefficients.

Vegetative BM significantly determined reproductive BM on a log–log R–V mixed-effect model (Table 5; Fig. 5). Species and the interaction between species and vegetative BM were not significant and were thus removed from the model (Table 5). The predicted log of reproductive BM increased with the log of vegetative BM (Table 5) with a positive intercept (0.7667). For both species, several points fell well below the regression lines, indicating a very low reproductive biomass for these values of vegetative plant BM, having a broad single point distribution (Supplementary Data Fig. S2).

Table 5.

Complete and simplified mixed-effect model built for reproductive biomass (fruit BM). The results include estimation, standard error (s.e.), and test of effects with t-statistics, degrees of freedom (df), and P-value (tdf (P-value)). The significance of the P-value is based on α = 0.05; values in bold are significant in the main model. BM = biomass, VA = V. angustifolium, VM = V. myrtilloides.

Model Effet Species Estimation (s.e.) Test
Complete Intercept 0.8381 (0.4137) 2.03 50  (0.0481)
Vegetative BM 0.6519 (0.1492) 4.37 475  (<0.0001)
Species VA -0.0880 (0.4309) -0.20475 (0.8383)
Species VM 0.0000 (0.0000)
Vegetative BM × Species VA 0.0321 (0.1676) 0.19475 (0.8481)
Vegetative BM × Species VM 0.0000 (0.0000)
Simplified Intercept 0.7667 (0.2280) 3.36 5.03  (0.0198)
Vegetative BM 0.6780 (0.0674) 10.05 477  (<0.0001)

Fig. 5.

Fig. 5.

Change in the log of reproductive biomass (g fresh weight), i.e. fruit BM - R, predicted by the R–V mixed-effect model according to log of vegetative BM (g dry weight), i.e. above-ground plant BM - V. BM: biomass, FM: fresh BM, DM: dry BM.

DISCUSSION

In this study, we assessed the phenological differences of two species of Vaccinium and the links between phenology and plant allometry, including the allometric traits of fruit. In the harvesting year, we observed marked differences in leaf and flower phenology between V. angustifolium and V. myrtilloides; phenological events occurred later for V. myrtilloides. We highlighted the importance of plant allometry, especially bud allometric traits, to explain some of these phenological differences, in agreement with our first hypothesis (leaf and flower phenology are linked to the plants’ allometric traits and species). Despite differences in terms of bud number and bud characteristics (e.g. the number of flowers per buds and total flower number that influence phenology and the number of produced fruits), reproductive biomass was similar for both species. Plant above-ground biomass determined fruit biomass (Weiner et al., 2009; Wenk and Falster, 2015); therefore, we only partially accept our second hypothesis (both phenology and plant allometry are predictors of fruit production). Delayed phenology can increase reproductive biomass indirectly by protecting flower buds from spring frost and favour reproductive success due to improved pollination (Jackson et al., 1972; Olson and Eaton, 2001). Thus, allometric traits, determined by specific plant architecture and phenology, influence the production of fruit, and V. myrtilloides represents a promising species due to its delayed phenology, slightly greater vegetative biomass and greater number of flowers relative to V. angustifolium.

Link between species, phenology and allometric characteristics

We only observed phenological differences between V. angustifolium and V. myrtilloides during the harvesting year, not during the pruning years, even under the dissimilar environmental conditions between 2017 and 2018 (Table 1). Smith (1969) highlighted the later leaf and flower phenology of V. myrtilloides in northern regions but did not cite any explanation apart from genetic differences. Although these species have distinct genetics and chromosome numbers, V. angustifolium being tetraploid with 48 chromosomes and V. myrtilloides being diploid with 24 chromosomes (Smith, 1969; Vander Kloet, 1988; Sakhanokho et al., 2018) – elements that could, in part, explain the phenological differences we observed no major phenological differences in the emerging leaf buds during the pruning years. This similar phenology between Vaccinium species during the pruning years suggests that this process depends highly on the mobilization of stored carbohydrates in the plant rhizomes, i.e. starch and sugars, made available for new shoot production following the stress of pruning (Hall et al., 1972; Janes, 2004; Morin, 2008). The delayed phenology observed for V. myrtilloides during the harvesting year, however, possibly indicates an effect of carbon partitioning through plant allometry (e.g. the number of leaf buds, total flower number and flower per bud). Although our SEM represented only a small part of the variability in the leaf and flower P(50) – bud phenology depends on several other internal and external factors (Badeck et al., 2004; Bell, 2009; Anna and Rufus, 2012) – the number of meristems partially influenced the phenological timing of the two species and their representative fruit production (see the following section).

During the pruning years, when the photosynthetic structures are ready, carbohydrate production in Vaccinium sp. is used preferentially to increase plant biomass and produce both flower and leaf buds (Swain and Darnell, 2001; Petridis et al., 2018). The production of reserves in stems and rhizomes occurs toward the end of summer until leaf senescence (Kaur et al., 2012). Thus, while the two species shared similar plant allometric traits, such as biomass, height, the number of ramifications and SLA, the observed differences in bud allometry during the harvesting year originated in the bud formation during the pruning year and was not related to a difference in reserves within the rhizomes. The interspecific allometric differences in flowering are established when flower buds are developed and where several pre-flowers are produced for the flower and fruit production of the following year (Vander Kloet and Hall, 1981; Kovaleski et al., 2015). Even if V. myrtilloides produces fewer flower buds, this species produces more flowers per bud, thereby allowing it to have a greater number of total flowers during the harvesting year and thus increased fruit numbers. Similarly, compared to V. angustifolium, V. myrtilloides produced more vegetative buds at the end of the pruning year, allowing greater branch production during the harvesting year. Although we did not record any photosynthetic data, we assume that both species had similar photosynthesis rates due to their comparable SLA, given the strong correlation between SLA and photosynthesis rate (Reich et al., 1997; Wright et al., 2004).

Sugar allocation has a direct role in bud phenology. In herbaceous and shrub plants, such as peas (Pisum sativum) (Mason et al., 2014) and roses (Rosa hybrida) (Barbier et al., 2015), respectively, decapitation of the apex leads to rapid auxiliary bud release because of a reduced sink competition between the apex and the lower dormant buds that receive more sucrose after excision. Moreover, at high levels of sucrose, auxiliary rosebuds open more rapidly, whereas low levels of sucrose result in a 3-d lag (Barbier et al., 2015). Although rhizome growth and biomass may have differed between the species (to date, we are not aware of any studies that compare their below-ground biomass), the starch reserves are shared between different developing shoots. In general, rhizomes act more as a carbon source (Hall et al., 1972; Janes, 2004; Morin, 2008), especially during shoot growth where starch reserves are severely depleted but are quickly refilled when growth is complete. Therefore, assuming a similar mobilization of stored carbohydrates from the plant rhizomes, such as during pruning years, the non-structural carbon partitioning in the buds of V. angustifolium and V. myrtilloides differed, in part, because of their above-ground allometry. Vaccinium angustifolium had fewer leaf buds leading to a decreased sink competition and thus a higher sugar allocation per bud. As observed for other plant species (Mason et al., 2014; Barbier et al., 2015; Deslauriers et al., 2019), a greater amount of carbohydrates per bud could explain the earlier bud burst, i.e. a lower number of vegetative meristems anticipate leaf P(50), for V. angustifolium compared to V. myrtilloides. However, unlike leaf buds, flower phenology was not related to flower bud number (not significant, Supplementary Data Table S2). Rather, the number of flowers per bud influenced both flower P(50) and leaf P(50), i.e. a lower number of flower units per bud anticipated for both P(50). This result thus corresponds to the delayed phenology in V. myrtilloides (Smith, 1969), a species having more flowers per bud.

Although the total flower number and number of flowers per bud were highly correlated (ρ = 0.70, data not shown), these traits had opposite effects on flower P(50). The effect of total flower number (standardized coefficient of −0.26, anticipating effect) was stronger and opposite to that of the number of flowers per bud (0.16, delaying effect). These opposite effects run counter to our hypothesis but could be explained by flower bud allometry: (1) several single flowers would require fewer resources and so earlier phenology compared to a grouped unit of flowers needing a greater amount of resources to develop, thereby increasing sink competition (Baïram et al., 2019); and (2) a flower bud having more units could require a higher degree of vascularization, which may require more time to develop compared to a flower bud having fewer flower units (Baïram et al., 2019).

Due to resource partitioning between reproductive and vegetative meristems, a higher leaf bud number tends to delay flower P(50). This positive link between leaf bud and flower P(50) is explained by the ability to quickly grow green leaves that assimilate CO2 and speed up the entire growth process when more leaves are produced. This latter phenomenon also explains the strong covariance between flower P(50) and leaf P(50). During the harvesting year, the first phases of flower phenology occurred earlier than leaf phenology; in both species, however, leaf bud burst (Stage 6, leaf completely open, Supplementary Data Fig. S4) occurred prior to the first flower opening (Stage 6, Fig. S5) (Shipley, 2002; Weraduwage et al., 2015). During the harvesting year, however, the reproductive parts compete for carbohydrates with vegetative parts of the plant, although reproduction often has priority with respect to the other sinks (Swain and Darnell, 2001; Chang et al., 2017). The more active and reproductive buds will develop into fruits, and this will be reflected in the sink competition and carbon allocations (Gauci et al., 2009; Kaur et al., 2012). Our results showed that vegetative growth (e.g. leaves, branches) slowed when fruit growth occurred, as the plant preferentially allocated carbohydrates to fruit development. Similar patterns have been observed for other species, including coffee, peach, cucumber and tomato (Marcelis, 1993; Heuvelink, 1996; Génard et al., 2008).

How plant allometry and phenology determine fruit production

Our SEM results show that the production of more flowers leads to a higher total fruit number and a higher fruit biomass per plant, in agreement with Usui (1994) and Usui et al. (2005). Thus, the number of fruits strongly and directly influences fruit biomass. However, fruit biomass decreased slightly under a delayed flower P(50). Earlier flower phenology thus seems to increase the time required for fruit development, thereby increasing a fruit’s biomass. Nonetheless, flower phenology had a much greater direct influence on fruit biomass during the period when the flowers were accessible for pollination; in our study, the number of added bees present in the field decreased sharply after the removal of the hives on June 28, 2018. Pollination was likely to have been greatly reduced after this date, meaning that flowers having a later phenology (e.g. V. myrtilloides) may not have had maximal pollination, thereby limiting ovule fertilization success by pollen vectors and thus the number of formed seeds. As fruit size is closely correlated with seed number (Aalders and Hall, 1961; Jackson et al., 1972; Myra et al., 2004), a delayed flower phenology can limit fruit biomass. Moreover, this relationship only holds when there are no early frost events; late reproductive phenology can protect flower buds against early spring frosts, which are a major factor affecting wild blueberry yields between years (Olson and Eaton, 2001; Strik and Yarborough, 2005; Gagnon et al., 2014). Other than the time for development reflected by phenology, insect pollinators, such as bees, are critical for seed production success and fruit biomass.

While the total number of produced fruits was higher in V. myrtilloides, the fruits were smaller than those of V. angustifolium. Both carbon allocation and pollination success can explain this difference. Plant allometry is linked directly to plant allocation, and this is essentially size-dependent (Weiner et al., 2009; Wenk and Falster, 2015). In shrubs such as Vaccinium sp., above-ground vegetative biomass is represented mainly by the photosynthetic biomass (i.e. leaves), while shoots and twigs are less important contributors. However, below-ground biomass represents >90 % of the total plant biomass (Marty et al., 2019) and contributes to the carbon requirements, especially at the time of shoot growth. The below-ground reserves are shared between the different developing shoots, thus limiting the effect on a single shoot (Morin, 2008). Reproductive biomass increases with above-ground biomass in a log–log allocation model, the R–V model (Weiner et al., 2009). When plant biomass increases, potential reproduction output also increases; however, there is also a greater structural and metabolic cost that limits maximizing carbon allocation to reproduction, depending on the source–sink carbon ratio (Gauci et al., 2009; Jorquera-Fontena et al., 2016, 2018). In our R–V mixed-effect model, this pattern was represented by a slope <1 (Weiner et al., 2009; Wenk and Falster, 2015) with no minimum size for reproduction (negative x-intercept). This balance between the source–sink carbon ratio was also represented in the SEM results by the direct and positive link between leaf P(50) and total fruit number (standardized coefficient of 0.10). An earlier leaf development limits the total fruit number by allocating more resources to the vegetative structures than productive structures. Therefore, to attain greater fruit production, the maximum plant biomass must be reached within a short time interval to avoid allocation overlap between the vegetative and reproductive structures. For a similar above-ground biomass, both Vaccinium species had similar reproductive outputs in terms of fruit biomass, despite differences in fruit size and number. Nonetheless, a large reproductive allocation was observed for a given vegetative biomass (i.e. a large point distribution around the regression lines, Supplementary Data Fig. S2). According to Bonser and Aarssen (2009), reproductive output also integrates developmental, genotypic and environmental factors, creating a large reproductive allometry, represented here by fruit biomass. Marked reproductive output at a given size could also be related to other factors, such as pollination. Indeed, reduced pollination success could explain the lower biomass per fruit in V. myrtilloides (Jackson et al., 1972). As mentioned above, fruit size is closely correlated with seed number, resulting from successful ovule fertilization by pollen vectors (Aalders and Hall, 1961; Jackson et al., 1972; Myra et al., 2004). Reduced pollination success is therefore related to smaller fruits as the smaller fruit of V. myrtilloides may hold fewer seeds (Aalders and Hall, 1961; Jackson et al., 1972). This limited pollination could be related to the reduced bee presence during the late phenology of V. myrtilloides (as discussed above) but also to the lower number of individuals of V. myrtilloides in our study fields. Moreover, because there is only 3 d of overlap in flower phenology between the two species, V. myrtilloides could not benefit from a large seed production by cross-pollination with V. angustifolium. Hybridization between species, however, can reduce reproductive biomass, and evidence of this was the several points lying below the regression line in our R–V model (Fig. S7), i.e. very low reproductive biomass relative to above-ground biomass. As proposed by Weiner et al. (2009), these represent cases of unsuccessful or aborted hybrid reproductive growth. In more southern regions, multiple studies have shown a deleterious effect on fruit production with the presence of both blueberry species in the same field due to this cross-pollination or inbreeding effect (Aalders and Hall, 1961; Schott, 2000; Bell et al., 2010).

CONCLUSIONS

We have demonstrated that the difference in allometric traits between two Vaccinium species can modulate both phenology and fruit production. Plants having a greater vegetative biomass, characterized by a greater plant height, branch length and number of leaves, produce more flowers and thus a higher fruit biomass. These findings are of great importance because a plant architecture having more vegetative and reproductive structures is going to present a sink competition in those structures that reduced carbon allocation, and a delayed leaf and flower bud phenology protected buds from early spring frosts. Vaccinium myrtilloides has an architecture that promotes both greater fruit production, in terms of number, and a delayed phenology. This study provides new perspectives on how to improve the reproductive output of Vaccinium by enhancing both vegetative biomass and plant architecture.

SUPPLEMENTARY DATA

Supplementary data are available online at https://academic.oup.com/aob and consist of the following. Table S1. Crop management calendar, treatment information and date of data collection for each studied site. Table S2. Structural equation model regression parameters. Figure S1. Schematic diagrams of the experimental design. Figure S2. Development of allometric traits of blueberry plants in time. Figure S3. Phenological stage of Vaccinium sp. – leaf in pruning year. Figure S4. Phenological stage of Vaccinium sp. – leaf in harvesting year. Figure S5. Phenological stage of Vaccinium sp. – flower in harvesting year. Figure S6. Phenological stage of Vaccinium sp. – fruit in harvesting year. Figure S7. R–V mixed effect model showing the relationship between the log reproductive BM (i.e. fruit BM – R), and the log vegetative BM (i.e. above-ground plant BM) with data for each species. Table SM1. Shapiro–Wilk test of normality with P values and result of each variable used. Table SM2. Result of linear regression for each variable estimate: equation, R2 and analysis of the variance of the linear fit. Figure SM1. The three regressions of the estimation produced.

mcaa083_suppl_Supplementary_Material

ACKNOWLEDGEMENTS

We thank the Corporation d’Aménagement Forêt Normandin (CAFN), who provided access to their sites and infrastructure, and we thank the Club Conseil Bleuet (CCB) and Agriculture and Agri-Food Canada (AAFC) employees for their technical assistance.

FUNDING

We thank the Syndicat des Producteurs de Bleuets du Québec (SPBQ), the Natural Sciences and Engineering Research Council of Canada (NSERC) (Grant RDCPJ-503182-16), and the Fonds de recherche axé sur l’agriculture nordique (FRAN-02) for their financial support. M.-P.F. also thanks the NSERC Canada Graduate Scholarships Master’s Program.

LITERATURE CITED

  1. Aalders LE, Hall IV. 1961. Pollen incompatibility and fruit set in lowbush blueberries. Canadian Journal of Genetics and Cytology  3: 300–307. [Google Scholar]
  2. Aarssen LW. 2008. Death without sex – the ‘problem of the small’ and selection for reproductive economy in flowering plants. Evolutionary Ecology  22: 279–298. [Google Scholar]
  3. Anna KK, Rufus I. 2012. Predicting flower phenology and viability of highbush blueberry. Journal of the American Society for Horticultural Science  47: 1291–1296. [Google Scholar]
  4. Badeck F-W, Bondeau A, Bottcher K, et al.  2004. Responses of spring phenology to climate change. New Phytologist  162: 295–309. [Google Scholar]
  5. Baïram E, Lemorvan C, Delaire M, Buck-Sorlin G. 2019. Fruit and leaf response to different source–sink ratios in Apple, at the scale of the fruit-bearing branch. Frontiers in Plant Science  10: 1039. [DOI] [PMC free article] [PubMed] [Google Scholar]
  6. Barbier F, Péron T, Lecerf M, et al.  2015. Sucrose is an early modulator of the key hormonal mechanisms controlling bud outgrowth in Rosa hybrida. Journal of Experimental Botany  66: 2569–2582. [DOI] [PMC free article] [PubMed] [Google Scholar]
  7. Barthélémy D, Caraglio Y. 2007. Plant architecture: a dynamic, multilevel and comprehensive approach to plant form, structure and ontogeny. Annals of Botany  99: 375–407. [DOI] [PMC free article] [PubMed] [Google Scholar]
  8. Beaujean AA. 2014. Latent variable modeling using R: A step-by-step guide. Abingdon: Routledge. [Google Scholar]
  9. Bell DJ. 2009. Spatial and genetic factors influencing yield in lowbush blueberry (Vaccinium angustifolium Ait.) in Maine. PhD thesis, The University of Maine. [Google Scholar]
  10. Bell DJ, Rowland LJ, Stommel J, Drummond FA. 2010. Yield variation among clones of lowbush blueberry as a function of genetic similarity and self-compatibility. Journal of the American Society for Horticultural Science  135: 259–270. [Google Scholar]
  11. Bonser SP, Aarssen LW. 2003. Allometry and development in herbaceous plants: functional responses of meristem allocation to light and nutrient availability. American Journal of Botany  90: 404–412. [DOI] [PubMed] [Google Scholar]
  12. Bonser SP, Aarssen LW. 2009. Interpreting reproductive allometry: individual strategies of allocation explain size-dependent reproduction in plant populations. Perspectives in Plant Ecology, Evolution and Systematics  11: 31–40. [Google Scholar]
  13. Chang TG, Zhu XG, Raines C. 2017. Source–sink interaction: a century old concept under the light of modern molecular systems biology. Journal of Experimental Botany  68: 4417–4431. [DOI] [PubMed] [Google Scholar]
  14. Chiasson G, Agrall J. 1996. Feuillet d’information A.2: Croissance et développement du bleuet sauvage. Fredericton: Ministère de l’Agriculture et de l’Aménagement rural du Nouveau-Brunswick. [Google Scholar]
  15. Deslauriers A, Fournier MP, Cartenì F, Mackay J. 2019. Phenological shifts in conifer species stressed by spruce budworm defoliation. Tree Physiology  39: 590–605. [DOI] [PubMed] [Google Scholar]
  16. Fournier M-P. 2020. Dynamique de la phénologie, de l’allométrie et du rendement des bleuetiers nains sauvages du québec selon l’espèce et divers traitements agricoles. MSc Thesis, Université du Québec à Chicoutimi. [Google Scholar]
  17. Gagnon S, Robitaille S, Ferland C, Lauzon L. 2014. Guide de production du bleuet sauvage. Québec: Centre de référence en agriculture et agroalimentaire du Québec (CRAAQ). [Google Scholar]
  18. Gauci R, Otrysko B, Catford JG, Lapointe L. 2009. Carbon allocation during fruiting in Rubus chamaemorus. Annals of Botany  104: 703–713. [DOI] [PMC free article] [PubMed] [Google Scholar]
  19. Génard M, Dauzat J, Franck N, et al.  2008. Carbon allocation in fruit trees: from theory to modelling. Trees  22: 269–282. [Google Scholar]
  20. Hall I, Forsyth F, Aalders L, Jackson L. 1972. Physiology of the lowbush blueberry. Economic Botany  26: 68–73. [Google Scholar]
  21. Hancock JF. 2008. Temperate fruit crop breeding: Germplasm to genomics. Dordrecht: Springer. [Google Scholar]
  22. Hartmann H, Trumbore S. 2016. Understanding the roles of nonstructural carbohydrates in forest trees - from what we can measure to what we want to know. The New Phytologist  211: 386–403. [DOI] [PubMed] [Google Scholar]
  23. Heuvelink E. 1996. Dry matter partitioning in tomato: validation of a dynamic simulation model. Annals of Botany  77: 71–80. [Google Scholar]
  24. Hooper D, Coughlan J, Mullen MR. 2008. Structural equation modelling: guidelines for determining model fit. Electronic Journal of Business Research Methods  6: 53–60. [Google Scholar]
  25. IBM Corp 2017. IBM SPSS advanced statistics 25. Armonk: IBM Corp. [Google Scholar]
  26. Jackson L, Aalders L, Hall I. 1972. Berry size and seed number in commercial lowbush blueberry fields of Nova Scotia. Canadian Field-Naturalist  99: 615–619. [Google Scholar]
  27. Janes DE. 2004. Carbohydrate dynamics of the wild blueberry floral bud (Vaccinium angustifolium Aiton). MSc Thesis, Dalhousie University. [Google Scholar]
  28. Jorquera-Fontena E, Alberdi M, Reyes-Diaz M, Franck N. 2016. Rearrangement of leaf traits with changing source–sink relationship in blueberry (Vaccinium corymbosum L.) leaves. Photosynthetica  54: 508–516. [Google Scholar]
  29. Jorquera-Fontena E, Pastenes C, Meriño-Gergichevich C, Franck N. 2018. Effect of source/sink ratio on leaf and fruit traits of blueberry fruiting canes in the field. Scientia Horticulturae  241: 51–56. [Google Scholar]
  30. Kaur J, Percival D, Hainstock LJ, Privé J-P. 2012. Seasonal growth dynamics and carbon allocation of the wild blueberry plant (Vaccinium angustifolium Ait.). Canadian Journal of Plant Science  92: 1145–1154. [Google Scholar]
  31. Körner C. 2003. Carbon limitation in trees. Journal of Ecology  91: 4–17. [Google Scholar]
  32. Kovaleski AP, Williamson JG, Olmstead JW, Darnell RL. 2015. Inflorescence bud initiation, development, and bloom in two southern highbush blueberry cultivars. Journal of the American Society for Horticultural Science  140: 38–44. [Google Scholar]
  33. Lacointe A. 2000. Carbon allocation among tree organs: a review of basic processes and representation in functional–structural tree models. Annals of Forest Science  57: 521–533. [Google Scholar]
  34. Li T, Heuvelink E, Marcelis LF. 2015. Quantifying the source–sink balance and carbohydrate content in three tomato cultivars. Frontiere Plant Science  6: 1–10. [DOI] [PMC free article] [PubMed] [Google Scholar]
  35. Lin W, Pliszka K. 2003. Comparison of spring frost tolerance among different highbush blueberry (Vaccinium corymbosum L.) cultivars. Acta Horticulturae  626: 329–333. [Google Scholar]
  36. Loescher WH, McCamant T, Keller JD. 1990. Carbohydrate reserves, translocation, and storage in woody plant roots. Journal of the American Society for Horticultural Science  25: 274–281. [Google Scholar]
  37. Marcelis L. 1993. Fruit growth and biomass allocation to the fruits in cucumber. 1. Effect of fruit load and temperature. Scientia Horticulturae  54: 107–121. [Google Scholar]
  38. Marcelis LFM, Heuvelink E. 2007. Concepts of modelling carbon allocation among plant organs. In: Vos J, Marcelis LFM, de Visser PHB, Struik PC, Evers JB, eds. Functional–structural plant modelling in crop production.  Dordrecht: Springer Netherlands, 103–111. [Google Scholar]
  39. Marty C, Lévesque JA, Bradley RL, Lafond J, Paré MC. 2019. Contrasting impacts of two weed species on lowbush blueberry fertilizer nitrogen uptake in a commercial field. PLoS One  14: e0215253. [DOI] [PMC free article] [PubMed] [Google Scholar]
  40. Mason MG, Ross JJ, Babst BA, Wienclaw BN, Beveridge CA. 2014. Sugar demand, not auxin, is the initial regulator of apical dominance. Proceedings of the National Academy of Sciences USA  111: 6092–6097. [DOI] [PMC free article] [PubMed] [Google Scholar]
  41. Ministère de l’Agriculture, des Pêcheries et de l’Alimentation du Québec (MAPAQ) 2016. Monographie de l’industrie du bleuet sauvage au Québec. Québec: Gouvernement du Québec. [Google Scholar]
  42. Morin C. 2008. Étude morphologique et physiologique du rhizome du bleuet nain: une contribution à l’amélioration de la régie de culture. MSc Thesis, Université Laval. [Google Scholar]
  43. Myra M, MacKenzie K, Vander Kloet SP. 2004. Investigation of a possible sexual function specialization in the lowbush blueberry (Vaccinium angustifolium Aiton. Ericaceae). Small Fruits Review  3: 313–324. [Google Scholar]
  44. Olson RA, Eaton LJ. 2001. Spring frost damage to placental tissues in lowbush blueberry flower buds. Canadian Journal of Plant Science  81: 779–781. [Google Scholar]
  45. Park JY, Canam T, Kang KY, Unda F, Mansfield SD. 2009. Sucrose phosphate synthase expression influences poplar phenology. Tree Physiology  29: 937–946. [DOI] [PubMed] [Google Scholar]
  46. Petridis A, van der Kaay J, Chrysanthou E, McCallum S, Graham J, Hancock RD. 2018. Photosynthetic limitation as a factor influencing yield in highbush blueberries (Vaccinium corymbosum) grown in a northern European environment. Journal of Experimental Botany  69: 3069–3080. [DOI] [PMC free article] [PubMed] [Google Scholar]
  47. Reich PB, Walters MB, Ellsworth DS. 1997. From tropics to tundra: global convergence in plant functioning. Proceedings of the National Academy of Sciences USA  94: 13730–13734. [DOI] [PMC free article] [PubMed] [Google Scholar]
  48. Rosseel Y. 2012. Lavaan: an R package for structural equation modeling and more. Version 0.5–12 (BETA). Journal of Statistical Software  48: 1–36. [Google Scholar]
  49. Sakhanokho HF, Rinehart TA, Stringer SJ, Islam-Faridi MN, Pounders CT. 2018. Variation in nuclear DNA content and chromosome numbers in blueberry. Scientia Horticulturae  233: 108–113. [Google Scholar]
  50. Scherrer B. 2007. Biostatistique. Montréal: G. Morin. [Google Scholar]
  51. Schott G. 2000. The nature of infertility and response to inbreeding in Vaccinium (blueberry) species. PhD Thesis, Michigan State University. [Google Scholar]
  52. Shipley B. 2002. Trade-offs between net assimilation rate and specific leaf area in determining relative growth rate: relationship with daily irradiance. Functional Ecology  16: 682–689. [Google Scholar]
  53. Smith D. 1969. A taximetric study of Vaccinium in northeastern Ontario. Canadian Journal of Botany  47: 1747–1759. [Google Scholar]
  54. Strik BC, Yarborough D. 2005. Blueberry production trends in North America, 1992 to 2003, and predictions for growth. HortTechnology  15: 391–398. [Google Scholar]
  55. Swain PAW, Darnell RL. 2001. Differences in phenology and reserve carbohydrate concentrations between dormant and nondormant production systems in southern highbush blueberry. Journal of the American Society for Horticultural Science  126: 386–393. [Google Scholar]
  56. Usui M. 1994. The pollination and fruit production on plants in the boreal forest of northern Ontario with special reference to blueberries and native bees. MSc Thesis, University of Guelph. [Google Scholar]
  57. Usui M, Kevan PG, Obbard M. 2005. Pollination and breeding system of lowbush blueberries, Vaccinium angustifolium Ait. and Vaccinium myrtilloides Michx.(Ericacaeae), in the boreal forest. The Canadian Field-Naturalist  119: 48–57. [Google Scholar]
  58. Vander Kloet SP. 1988. The genus Vaccinium in North America. Ottawa: Agriculture Canada, Gouvernement du Canada. [Google Scholar]
  59. Vander Kloet SP, Hall IV. 1981. The biological flora. 2. Vaccinium myrtilloides Michx., velvet-leaf blueberry. The Canadian Field-Naturalist. 95: 329–345. [Google Scholar]
  60. Weiner J. 2004. Allocation, plasticity and allometry in plants. Perspectives in Plant Ecology, Evolution and Systematics  6: 207–215. [Google Scholar]
  61. Weiner J, Campbell LG, Pino J, Echarte L. 2009. The allometry of reproduction within plant populations. Journal of Ecology  97: 1220–1233. [Google Scholar]
  62. Wenk EH, Falster DS. 2015. Quantifying and understanding reproductive allocation schedules in plants. Ecology and Evolution  5: 5521–5538. [DOI] [PMC free article] [PubMed] [Google Scholar]
  63. Weraduwage SM, Chen J, Anozie FC, Morales A, Weise SE, Sharkey TD. 2015. The relationship between leaf area growth and biomass accumulation in Arabidopsis thaliana. Frontiers in Plant Science  6: 1–21. [DOI] [PMC free article] [PubMed] [Google Scholar]
  64. Wright IJ, Reich PB, Westoby M, et al.  2004. The worldwide leaf economics spectrum. Nature  428: 821–827. [DOI] [PubMed] [Google Scholar]
  65. Yarborough D. 2012. Establishment and management of the cultivated lowbush blueberry (Vaccinium angustifolium). International Journal of Fruit Science  12: 14–22. [Google Scholar]
  66. Yarborough D. 2015. Flower primordia development stage Available at: https://extension.umaine.edu/blueberries/factsheets/irrigation/flower-primordia-development-stage/ (7 May 2019).
  67. Yarborough DE. 2004. Factors contributing to the increase in productivity in the wild blueberry industry. Small Fruits Review  3: 33–43. [Google Scholar]
  68. Zuur AF, Ieno EN, Elphick CS. 2010. A protocol for data exploration to avoid common statistical problems. Methods in Ecology and Evolution  1: 3–14. [Google Scholar]

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