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Article

Soil Water Content Directly Affects Bud Burst Rate in Single-Node Cuttings of Perennial Plants

by
Santiago Signorelli
1,2,*,
Juwita R. Dewi
3 and
Michael J. Considine
2,4
1
Laboratorio de Bioquímica, Departamento de Biología Vegetal, Facultad de Agronomía, Universidad de la República, Av. Garzón 780, Sayago CP, Montevideo 12900, Uruguay
2
The Centre of Excellence in Plant Energy Biology, School of Molecular Sciences, The University of Western Australia, 35 Stirling Highway, Crawley, WA 6009, Australia
3
School of Agriculture and Environment, The University of Western Australia, 35 Stirling Highway, Crawley, WA 6009, Australia
4
Horticulture and Irrigated Agriculture, The Department of Primary Industries and Regional Development, Perth, WA 6000, Australia
*
Author to whom correspondence should be addressed.
Submission received: 16 December 2021 / Revised: 24 January 2022 / Accepted: 27 January 2022 / Published: 31 January 2022
(This article belongs to the Special Issue Plant Responses to Stress and Environmental Stimulus)

Abstract

:
The use of single-node cuttings of shoots as explants to study bud dormancy and its physiology under controlled conditions is a common practice in grapevine (Vitis vinifera L.) or other perennial plant research. In particular, this method has been extensively used to understand the effect of different chemicals on bud dormancy and bud burst. However, the soil water content in those experiments is usually not reported and its relevance is often neglected. Here, we observed that an unevenly distributed soil water content in a tray containing multiple explants results in an uneven pattern of bud burst within the same treatment. Thus, we hypothesised that soil water content can dramatically affect bud burst. To investigate this, we first established that fresh single-node cuttings were able to transport water into the buds. We then tested the rate of bud burst at different water treatments (35%, 55%, 70%, 85%, and 100% of field capacity; FC). We observed a clear dependence of bud burst on water, in which, at very low levels of water, bud burst does not occur; after 35% FC, bud burst rate increases with water content until around 85% FC; and, from 85% FC, bud burst rate becomes independent of water content. These data highlight the critical importance of monitoring soil water content in any bud burst assay in perennials. Finally, we provide a detailed protocol for determining and controlling field capacity and other soil water content indicators.

1. Introduction

The use of explants of perennial plants is a common practice to evaluate kinetics of bud burst, for instance, to evaluate the depth of dormancy, the effect of environmental clues, or applied chemicals on bud burst [1,2,3,4]. The use of explants enables the use of controlled conditions, which is a major limitation when working with perennial plants, as well as removing the influence of dominance influences of the corpus and competing sinks. Despite the wide use of this methodology, the influence of water availability on bud burst has not been reported. This is particularly important because the application of chemicals usually implies adding water to the single-node cuttings, as water is the most common solvent used. In addition, the water content of soil in single-node cuttings experiments is commonly not reported. We hypothesise that soil water content can explain much of the stochastic variability observed in bud burst experiments and, thus, that determining a fixed water content within the experiments is critical to underpin the validity and reproducibility of data reported.
Water content in the soil is usually expressed as volumetric water content (VWC), gravimetric water content (GWC), or a percentage of field capacity (FC), which simply refers to the maximum amount of water that a soil can retain. VWC (Θv) is calculated as:
Θv = (Vwet − Vdry)/Vdry
Vwet being the volume of wet soil and Vdry the volume of dry soil. GWC (Θg) is calculated as:
Θg = (Wwet − Wdry)/Wdry
Wwet being the weight (mass) of wet soil and Wdry the weight of dry soil. Given that measuring mass is simpler than volume, GWC is generally preferred over VWC.
The objectives of this work were to evaluate the effect of soil water content on bud burst of grapevine single-node cuttings and to provide a protocol to eliminate water content as a variable in single-node cutting experiments. For this purpose, we determined whether uneven water content affects bud burst, whether dormant buds are able to take up water, and the kinetics of bud burst at different % of FC.

2. Materials and Methods

2.1. Preparation of Pots and Calculation of Field Capacity

The substrate of potting mix at pH~6.0, containing fine composted pine bark, coco peat, and brown river sand in the ratio of 2.5:1:1.5 (w/w), was homogenously mixed and distributed among 19 seedling trays on trays, each adjusted to a mass of 2500 g (Figure 3A). As the potting mix was not completely dry, three additional samples of around 30 g were used to determine the initial moisture content and, hence, initial dry weight. The 30 g samples were incubated in an oven at 105 °C for two days to determine the dry weight (Figure 3B). Once the moisture was determined in the subsamples, the dry weight of the soil in each tray was calculated (Figure 3C). Out of the 19 trays, 15 were used for planting three replicates of the five treatments described below. The remaining four trays were used to determine FC. The FC trays were saturated with water and left in the washing area where they were able to drain (Figure 3D). After 3 h, the trays were placed on a stand with paper below to monitor more accurately the presence of dripping from the trays. Replacing the paper once wet and inspecting every 30 min, we determined the weight of the pots at field capacity when no more drops came out from the tray for 1 h (Figure 3E,F). Once 100% FC was established, the weight to achieve the different FC was calculated (Figure 3G).

2.2. Plant Material and Growth Conditions

Grapevine (Vitis vinifera L.) cv. Merlot canes containing mature, dormant buds from node 3 to 10 were collected from a commercial vineyard in Margaret River, Australia (34° S, 115° E) on the second week of June 2017 (winter in the south hemisphere). At that time, the local photoperiod was 10/14 h light/dark (sunrise 07:23 am, sunset 5:17 pm). On the collection day, the temperature was 18 °C/10 °C (high/low), the average temperature for the month was 13 °C, and the highest and lowest in that month were 23 °C (11 June) and 3 °C (9 June), respectively. The highest humidity was 96% (1 June) and 25% (9 June). The canes were wrapped on newspaper, externally moistened by spraying water, placed on black bags sealed with tape to be transported to the lab, and stored at 4 °C for 10 days. Single-node cuttings (explants) were cut about 4–5 cm below the node until 2–3 cm above the node, and immediately planted on the trays containing the potting mix described above. A total of 90 single-node cuttings were planted per treatment divided in three different trays (replicates). Before planting, water was added to each tray until reaching the exact weight for its corresponding treatment of field capacity %. Once the explants were planted, the new weight for each tray was recorded to know the new weight for the treatment tray considering the weight of the plant material. Explants were grown at 20 °C under a photoperiod of 12:12 h, illuminated with a photosynthetic photon flux density of 100 µmol·m−2·s−1, for 49 days. Explants were watered every day on a set of scales until reaching the corresponding weight of the tray, including the initial weight of the plant material, for each particular water treatment (Figure 3H).

2.3. Water Treatments

To assess the effect of soil water availability on bud burst, we defined five water treatments corresponding to 35%, 55%, 70%, 85%, and 100% of FC. Values below 35% of FC were not considered, as it is unlikely to have growth in such conditions when using an explant system (absence of roots).

2.4. Micro-Computed Tomographies

To investigate the buds’ water uptake capacity, buds were dissected from the cane and incubated overnight with caesium iodide (CsI) 10% at 4 °C or without CsI (control). 3D imaging using μCT was performed on each bud (BBCH scale: 00-01 [5]). The micro-computed tomographies (μCT) were performed with a nanofocus CT system (Phoenix Nanotom, General Electric, Heidelberg, Germany) after incubation. Buds were mounted on a rotation stage by means of a Parafilm wrap. A total of 2400 projection images per scan were taken with 0.15° angular steps for a full 360° rotation. Capture time for each image was 500 ms. Settings were 55 kV/182 μA for control samples and 60 kV/167 μA for CsI samples. Image pixel resolution was 2.50–3.25 μm. Slice reconstruction was performed by Octopus Reconstruction version 8.9.0.9 (XRE, Ghent, Belgium) using the filtered back-projection method.

3. Results

To determine if uneven distribution of water affects bud burst, we placed single-node cuttings on seedling trays on concave plastic trays, in which the water was preferably distributed towards the centre of the seedling trays (Figure 1). After 35 days, we observed that the bud burst was not spatially uniform, whereby bud burst of explants in the centre of the tray (dashed rectangle in Figure 1A) greatly exceeded those in the periphery (Figure 1). This was consistent with the hypothesis that water availability was an important variable affecting bud burst kinetics in single-node cutting experiments.
It is well documented that quiescent buds are isolated to prevent dehydration during winter, particularly through the restriction of aquaporin activity, plasmodesmata conductance, and apoplastic conductivity [6,7,8,9,10]. For water to have a direct effect on bud burst, it needs to be transported to the bud after transferring the single-node cutting to the seedling tray. Therefore, we tested if quiescent buds were able to transport water immediately after dissecting them from the cane. Using a contrast agent, and analysing μCT data, we observed that water was effectively transported through the bud 24 h after incubation (Figure 2).
Given the evidence presented by Figure 1 and Figure 2, we set up an experiment controlling the water content of the pots every day (Figure 3) for 47 days to see if different kinetics of bud burst are observed. Figure 3 explains all the steps required to control the water content in soil. In our case, we chose 35%, 55%, 70%, 85%, and 100% of FC to test if there is a correlation between bud burst and soil water content.
We observed a strong correlation between bud burst and water treatments (Figure 4). Explants grown on 100% and 85% FC had the greatest rate of bud burst, reaching 50% bud burst at about 24 d, followed by those at 70% FC, which reached 50% bud burst at 30 d. Bud burst of explants grown on 55% FC was considerably delayed, reaching 50% bud burst at 44 d, revealing how small variations in water content can make important differences in bud burst rates. Finally, explants grown on 35% FC did not reach 50% bud burst within the time evaluated (Figure 4A); only 8% of the buds had burst at the end of the experiment. The curves for 100% and 85% FC were almost indistinguishable, being only significantly different between day 25 and 33 (Figure 4A), where the curve for 100% FC reached higher values. Conversely, clear and significant differences were observed between all the other curves since the start of bud burst for each curve. Overall, the graph of Figure 4A suggests a triphasic behaviour between bud burst rate and water content of soil, in which, at very low levels of water (e.g., <35% FC), there is no correlation, as buds are not going to burst (i.e., a zero order kinetic for water), a second phase (e.g., 35–85% FC), in which there is a positive correlation between bud burst rate and water content, and a third phase (e.g., >85% FC), in which bud burst rate became, again, independent of water content (i.e., a zero-order kinetic for water), most likely because water was no longer a limiting factor and bud burst is determined by other factors.
To explore this triphasic behaviour further and investigate whether the positive correlation observed is linear, we plotted the days to reach 8% bud burst in relation to the % of FC (Figure 4B). In this case, the three kinetic phases are clearly identified and a linear correlation was observed for the second phase (Figure 4B), suggesting that the kinetic is of the first order (i.e., bud burst rate increases linearly with water content). After 85% FC, the time to reach 8% bud burst is the same as at 100%, confirming that the initiation of bud burst was not affected by water contents of soil above 85% of FC. It is important to note, however, that, if values as high as 90% bud burst are used, there may be an effect of water, as we observed that the buds at 100% of FC were the first to reach the plateau of nearly 100% bud burst (Figure 4A).

4. Discussion

This study aimed to test the often overlooked importance of water availability on bud burst kinetics in explant studies, which have become the main morphometric test for the depth of dormancy in perennating buds. The buds used in this study were collected towards the end of winter, and further stored at 4 °C prior to experimentation, in order to eliminate dormancy as a factor. Our results demonstrated that quiescent buds of explants can transport water as soon as they are subjected to water treatments (Figure 2) and that water availability can directly and strongly influence the rate of bud burst when provided within the range of 35 to 85% FC (Figure 4). For instance, a reduction of 15% FC can delay bud burst by ~50% time (i.e., from 30 days to 44 days to reach 50% BB). This demonstrates that a tight control of water content in soil is required when determining bud burst rate kinetics for comparing different treatments, as these differences observed by water can be much greater (i.e., ~10 days) than those sometimes observed by different exogenous treatments of molecules (e.g., 2–4 days). Therefore, we provided here an illustrative and detailed protocol (Figure 3) explaining how to determine the different percentages of FC when setting up the experiment and how to follow up the experiment. As FC here is expressed as % of mass of water by mass of substrate, a set of scales is required for these calculations. However, it is also possible to use volumetric units and express as volume of water per volume of substrate. We understand that the determination of volume is usually more complex in most laboratories. In our work, we presented all the data as % FC; however, it is also possible to express the data as GWC or VWC using the equations described in introduction. Alternatively, if the number of treatments represent a major constraint to control daily the water levels of the experiment, we suggest working always above 80–85% FC, a range in which, in our experimental conditions, bud burst takes place and becomes independent of water levels. Thus, we define this as a “safety zone” of water contents when comparing bud burst rates under different treatments, particularly important when the treatments of chemicals implicate the use of water. However, this “safety zone” should be ideally determined in each lab depending on the substrate used, because different substrates have a different water retention capacity, resulting in significant differences in water content relative to soil (i.e., GWC or VWC). In terms of GWC, 85% of FC in our system represented 0.94 gwater·gsoil−1 and 100% of FC was 1.11 gwater·gsoil−1.
Several earlier studies have illustrated the regulated changes in free and bound water [10], in the activity of aquaporin transporters [6,11], the role of plasmodesmata in dormancy transitions of perennating buds [7], the expansion of apoplastic connectivity upon bud burst [9], and the change dynamics in moisture content in the bud across the season [11]. The fact that water has a strong effect on bud burst in explant further supports the importance of those biological processes controlling water content in the bud, such as plasmodesmata regulation, aquaporins activity, etc. A deeper understanding of the signals controlling these mechanisms could allow scientists to develop managing practices to manipulate bud burst that can be used by farmers to synchronize bud burst better. Besides the biochemical mechanism regulating water transport, environmental clues can also affect water availability and transport to the bud. In grapevine, shade [12] and water deficit [13] were shown to reduce water transport capacity in field conditions, whereas high temperatures increase it [14]. The xylem network varies between grapevine cultivars; therefore, some cultivars have greater hydraulic conductivity than others (e.g., Thompson Seedless (high) vs. Merlot (low)) [15,16], as well as the xylem hydraulic response to environmental clues [15]. Likewise, in other perennials, several studies showed that frosting or cold temperatures affect water uptake and transport through the vascular system [17,18]. Therefore, it is expected that environmental clues modulate bud water content in perennials grown in the field. This aspect has not been less explored in research where xylem conductivity was investigated. However, a study conducted on apple trees, where soil frost was prolonged by soil insulation, has shown that the prolonged frost not only reduced water conductivity, but also buds’ water content, and this correlated with a delayed bud burst [17]. Hence, the conclusion of our study about the effect of water content on bud burst using an explant system is likely to be translatable to what occurs in field conditions.

5. Conclusions

Single-node cuttings containing quiescent buds are able to transport water, and water has a strong effect on the rate of bud burst. Therefore, we conclude that statements of water content must be included in experiments on bud burst in explants. Soil water content must be controlled in these experiments to avoid the variation in water contents that confounds the differences caused by the specific treatment by chemicals or environmental conditions in bud burst rates, and to avoid false positive effects.

Author Contributions

Conceptualisation, S.S.; methodology, S.S. and M.J.C.; formal analysis, S.S.; investigation, S.S. and J.R.D.; resources, M.J.C.; writing—original draft preparation, S.S.; writing—review and editing, S.S. and M.J.C.; funding acquisition, M.J.C. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the Australian Research Council Discovery Project DP150103211.

Acknowledgments

We thank Jeremy Shaw, Pieter Verboven, and Zi Wang, who contributed to the generation of microCT data. SS is a grateful member of the Uruguayan system of researchers (Sistema Nacional de Investigadores, SNI, Uruguay).

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 1. Irregular bud burst on a seedling tray with uneven distribution of water. (A) Representative picture of single-node cuttings after 35 days when water was not homogenously distributed across the tray. (B) Top view representation of the most hydrated area of the tray. (C) Lateral view representation of the tray showing the bending of the seedling tray and the water flux generated towards the centre.
Figure 1. Irregular bud burst on a seedling tray with uneven distribution of water. (A) Representative picture of single-node cuttings after 35 days when water was not homogenously distributed across the tray. (B) Top view representation of the most hydrated area of the tray. (C) Lateral view representation of the tray showing the bending of the seedling tray and the water flux generated towards the centre.
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Figure 2. Micro-computed tomographies (μCT) of buds 24 h after being dissected from the cane and incubated with or without contrast agents (CsI). (A) Top view section of a control bud without contrast agent. (B) Top view section of a bud incubated with the contrast agent. (C) Lateral view of a bud incubated with the contrast agent. The arrows indicate the contrast agent, which is observed as white colour. n = 3.
Figure 2. Micro-computed tomographies (μCT) of buds 24 h after being dissected from the cane and incubated with or without contrast agents (CsI). (A) Top view section of a control bud without contrast agent. (B) Top view section of a bud incubated with the contrast agent. (C) Lateral view of a bud incubated with the contrast agent. The arrows indicate the contrast agent, which is observed as white colour. n = 3.
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Figure 3. Procedure to determine and control the field capacity in soil and the control of in-soil water levels during the experiment. (AH) describe the successive steps of this protocol, being (A) step 1 and (H) step 8. The values shown in panel (G) are only for exemplification, and are not real data.
Figure 3. Procedure to determine and control the field capacity in soil and the control of in-soil water levels during the experiment. (AH) describe the successive steps of this protocol, being (A) step 1 and (H) step 8. The values shown in panel (G) are only for exemplification, and are not real data.
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Figure 4. Kinetics of bud burst at different water contents in soil expressed as % of FC. (A) Bud burst percentages for each water treatment. The curve represents a regression determined with the generalised additive model, with its 95% confidence level intervals for the prediction presented as the surrounding grey area. The dashed light-blue line marks the 8% bud burst threshold used to determine the days plotted in B. (B) Three kinetic behaviours of bud burst rate in relation to water content. The purple circles indicate the means and the grey circles indicate the independent replicates; the bigger the circle, the more replicates giving the same result (n = 3). The first phase indicates a range of water content in which bud burst was unlikely to happen due to water restrictions, where no data (ND) was collected.
Figure 4. Kinetics of bud burst at different water contents in soil expressed as % of FC. (A) Bud burst percentages for each water treatment. The curve represents a regression determined with the generalised additive model, with its 95% confidence level intervals for the prediction presented as the surrounding grey area. The dashed light-blue line marks the 8% bud burst threshold used to determine the days plotted in B. (B) Three kinetic behaviours of bud burst rate in relation to water content. The purple circles indicate the means and the grey circles indicate the independent replicates; the bigger the circle, the more replicates giving the same result (n = 3). The first phase indicates a range of water content in which bud burst was unlikely to happen due to water restrictions, where no data (ND) was collected.
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MDPI and ACS Style

Signorelli, S.; Dewi, J.R.; Considine, M.J. Soil Water Content Directly Affects Bud Burst Rate in Single-Node Cuttings of Perennial Plants. Agronomy 2022, 12, 360. https://0-doi-org.brum.beds.ac.uk/10.3390/agronomy12020360

AMA Style

Signorelli S, Dewi JR, Considine MJ. Soil Water Content Directly Affects Bud Burst Rate in Single-Node Cuttings of Perennial Plants. Agronomy. 2022; 12(2):360. https://0-doi-org.brum.beds.ac.uk/10.3390/agronomy12020360

Chicago/Turabian Style

Signorelli, Santiago, Juwita R. Dewi, and Michael J. Considine. 2022. "Soil Water Content Directly Affects Bud Burst Rate in Single-Node Cuttings of Perennial Plants" Agronomy 12, no. 2: 360. https://0-doi-org.brum.beds.ac.uk/10.3390/agronomy12020360

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