SEEFOR 13(1): early view
Article ID: 2201
ORIGINAL SCIENTIFIC PAPER
Acorn Yields and Seed Viability of Pedunculate Oak in a 10-year Period in Forest Seed Objects across Croatia
Anđelina Gavranović Markić1,*, Saša Bogdan2, Marija Gradečki Poštenjak3, Miran Lanšćak1, Zvonimir Vujnović1, Sanja Bogunović1, Mladen Ivanković1,*
(1) Croatian Forest Research Institute, Division of Genetics, Forest Tree Breeding and Seed Science, Cvjetno naselje 41, HR-10450 Jastrebarsko, Croatia;
(2) University of Zagreb, Faculty of Forestry and Wood Technology, Department of Forest Genetics, Dendrology and Botany, Svetošimunska 25, HR-10000 Zagreb, Croatia;
(3) Croatian Forest Research Institute, Division for Silviculture, Cvjetno naselje 41, HR-10450 Jastrebarsko, Croatia
Citation: Gavranović Markić A, Bogdan S, Gradečki Poštenjak M, Lanšćak M, Vujnović Z, Bogunović S, Ivanković M, 2022. Acorn Yields and Seed Viability of Pedunculate Oak in a 10-year Period in Forest Seed Objects across Croatia. South-east Eur for 13(1): early view. https://doi.org/10.15177/seefor.22-01.
Received: 5 Oct 2021; Revised: 8 May 2022; Accepted: 13 May 2022; Published online: 27 May 2022
Cited by: Crossref Google Scholar
Quercus robur L. exhibits not only a large inter-annual variability in seed production but also considerable variability among locations and individuals within the same year. The differences in how individual trees and populations of oaks invest in acorn production, both in terms of the yield size and the acorns quality, is of interest both ecologically and economically. For this research we used data collected from harvesting which has been organised and executed by the largest forestry company in Croatia - public enterprise Croatian Forests Ltd. According to the Act on Forest Reproductive Material, Croatian Forest Research Institute is designated as the Official Body that supervises production and provides analysis of quality of forest reproductive material. Regarding that, we summarized data of 10-year long records (from 2009 to 2018) of submitted seed samples and seed quality testing from 119 Q. robur forest seed objects across Croatia. Our aim was to investigate seed yield and effects of seed size and seed moisture content on seed viability. In the study period there were four years with higher quantity of collected seeds than other years (2010, 2011, 2015 and 2017). There was no significant difference in seed viability among forest seed objects. However, variations among years within forest seed objects were highly significant. It was also found that seed size (indicated by the number of acorns per kg) and seed moisture content were significantly related to seed viability. Bigger seed dimensions, i.e. lower mean number of acorns per kg, correlated with higher viability. Lower moisture content affected decrease in acorn viability. On average, viability dropped below 70% when acorn mean moisture decreased below 36%. Thus, it can be concluded that bigger seeds and seeds with moisture content of 40-44% have better viability.
Keywords: Quercus robur L.; acorn crop; moisture content; seed size
There is a growing interest in understanding (and being able to predict) seed yield, an essential prerequisite for successful stand regeneration and its further development. Since acorn production is a foundational process of ecosystems dominated by oaks, it is critical to the sustainable management of oak forests. For oaks, a defining characteristic are spatial-temporal variations in large synchronous but intermittent seed yields (Liebhold et al. 2004, Bogdziewicz et al. 2018). Synchrony is the extent to which seed crops are correlated across years, while temporal variability is the among-year variation in seed yield (Liebhold et al. 2004). Such synchronous seed production, which fluctuates strongly from year to year, is called masting and has been frequently documented in oak species (Kelly 1994, Greenberg and Parresol 2002).
The pedunculate oak begins fructification at the age of 40–50 years in the open and at the age of 70–80 years in dense canopies (Martiník et al. 2014). In general, a large acorn crop is expected every 6-9 years and a moderate crop every 3-4 years (Worrel and Nixon 1991, Harmer 1994). In any particular year, seed production varies among stands (Crawley and Long 1995, den Ouden et al. 2004, Kasprzyk et al. 2014, Pesendorfer et al. 2020). Even in poor crop years individual trees and stands will produce some seeds. Similarly, in good crop years, certain stands may fail to produce seeds (Harmer 1994, Wesołowski 2015). In addition to the high variation in seed production among years, there are also considerable variations among individual oaks within the same year (Caignard et al. 2019). The cause of periodic seed production is unclear, but likely related to an interaction between environmental, endogenous and biological factors over a longer period.
Besides quantity, a basic prerequisite for successful natural and artificial regeneration is the quality of seed (Poštenjak and Gradečki 2001, Gradečki-Poštenjak et al. 2018). It is possible to make visual assessment of acorn yield in August/September (Van der Meer et al. 2002), but the quality of seed crop cannot be known until seed dispersal in autumn. Quality of acorns is determined by many factors, including size, weight, moisture content, mineral nutrient reserves, and the percentage of seeds that germinate or are capable of germinating (seed viability) (Poštenjak and Gradečki 2001, Nikolić et al. 2006, Devetaković et al. 2019). A combination of environmental factors during seed development and the genetic variability can result in variations in seed dimensions (Willan 1985). Larger seed dimensions indicate better seed quality, germination and genetic potential (Toon et al. 1990, Davidson et al. 1996), but seed quality may depend on several factors, such as the time of the harvest (Bellari and Tani 1993), variation in the nutrient content (Abideen et al. 1993) and genetic factors (Farmer 1980, Jayasankar et al. 1999). After falling to the ground, the seeds should be promptly collected and cleaned. Prolonged time on the ground and suboptimal cleaning may adversely affect seed viability.
Generally, the lower the quality of the seeds, the faster they deteriorate. After harvesting, acorns have a moisture content ranging from 40% (Suszka et al. 2000, Szabla and Pabian 2009) to 50% (Aniszewska et al. 2020). Fresh acorns are specific because of high moisture content, and they do not tolerate moisture loss without adverse effect on its viability (Doody and O'Reilly 2008). The most relevant method for testing seed quality in practical forestry is testing the germination capacity of seeds (Bonner 1974a), but this method takes several weeks and for some species pre-treatment may take some additional weeks or months. On the other hand, the viability test, i.e. the topographical tetrazolium test, is a method that also allows the viability of seeds to be assessed accurately, but much more quickly than with the germination test. The viability test plays an important role in assessing the physiological quality of the seeds and the percentage of viability, and it provides valuable information for diagnosing possible problems with seed quality, such as mechanical damage and insect damage.
In the literature, mast years are referred to as years when acorns are produced in substantial quantities (Isagi et al. 1997, Sever et al. 2013). Greenberg and Parresol (2002) defined mast year as the year of production higher than the 5-year average production. In Croatia, the main problem is that there has not been long-term monitoring of the yield of forest trees, and it is not possible to precisely determine the actual production potential of individual forest stands. The current practice is that forest offices (FOs) and/or forest administrations (FAs) stop collecting seeds when they ensure and cover their own needs. To our knowledge, long-term monitoring of pedunculate oak crop in Croatia was conducted from 1976 to 1995 on a pedunculate oak stand in Lipovljani (Matić et al. 1996a), from 1968 to 1994 in a larger area of FA Vinkovci (Matić et al. 1996b), and from 2000 to 2016 in the Spačva Basin area (Gradečki-Poštenjak et al. 2011, Gradečki-Poštenjak 2017).
For this paper, we used data of a 10-year-long record of annual acorn yield (2009-2018) from 119 pedunculate oak forest seed objects (FSOs) across Croatia. Our objectives were to investigate (1) the quantity of pedunculate oak acorns (i.e. the number of seed samples) during 10 years in Croatia and to determine (2) the relationship between seed viability and moisture content and (3) the relationship between seed viability and seed size. To our knowledge, this is the first attempt to summarize the data on monitoring of the yield of one of the most important forest tree species in Croatia.
MATERIALS AND METHODS
Acorn crops were collected from 2009 to 2018 in 119 pedunculate oak FSOs (seed sources, seed stands) across Croatia. We used data collected from harvesting which has been organised and executed by the largest forestry company in Croatia – public enterprise Croatian Forests Ltd. Control of seed collection, sampling and quality testing was carried out by the Croatian Forest Research Institute (CFRI) – the Official Body according to the Act on Forest Reproductive Material (Official Gazette 75/09, 61/11, 56/13, 14/14, 32/19, 98/19). Sampling procedures and seed quality testing have been performed by the Laboratory for Seed Testing (LIS) of the CFRI according to International Rules for Seed Testing (ISTA Rules).
A seed lot (i.e. acorn crop harvested from the same FSO in a season) quality has been determined by analysing seed samples, which were assumed as representative parts of a crop. The seed lots were stored in such a way that all its parts were accessible for sampling, separated from other seed lots and marked so they could be easily identified. Issued lot and sample sizes for Quercus sp. are given in Table 1. The composite sample was formed by combining and mixing primary samples taken from different positions of a seed lot and subsamples, which were combined to create the submitted sample for moisture content.
Table 1. ISTA Rules: Table 2C Part 2 – Lot sizes and sample sizes: Tree and shrub species (part) (ISTA).
Table 2. Basic descriptive statistics of studied acorn crop traits from selected FSOs in FOs across various years.
Samples were sealed and labelled according to the following data: species, register number of forest seed object, number of the package/total number of packages constituting the composite sample, total weight of the seed lot, and weight of the seed sample or the number of seeds in the sample. The submitted samples were transferred to the LIS as soon as possible.
The Laboratory Procedure
The following analyses were conducted on all seed samples: purity analysis, thousand-seed weight (TSW) determination, moisture content (MC), and topographical tetrazolium test for seed viability (SV). The objective of the purity analysis was to determine weight proportion of pure seeds in a sample (pedunculate oak acorns without any other seeds or matters like twigs, leaves etc.). It was the first analysis to be carried out and subsequent analyses were made on the pure seed component of the sample. The working sample for TSW determination consisted of 400 pure seeds taken randomly and determined by mean of eight replicates, each containing 50 seeds. The MC was measured according to the ISTA low-temperature oven method. Seeds were dried in a forced ventilated oven at 103 °C for 17 h. The difference between a fresh sample weight and its oven-dried weight divided by the fresh weight was recorded as the sample moisture content proportion. Acorn SV was examined with the tetrazolium method. The seeds were soaked in 2,3,5-Triphenyl tetrazolium chloride, which is an indicator of cellular respiration. Viable seeds were stained while non-viable seeds remained white. The proportion of stained acorns in a sample was a sign of its viability.
In order to calculate the number of acorns per kg (N·kg-1) in the original seed lot from which the submitted sample was taken, the following formula was applied (Forestry Commission 2018):
N of seeds per kg (N·kg-1) = 1000/T x 1000 x P/1000
where T is 1000 pure seed weight in grams and P is purity % from the purity test.
Finally, data on seed sample moisture content (MC %), seed sample viability (SV %) and number of acorns·kg-1 per sample (N·kg-1 – indicating acorn size) were further processed.
Data Processing and Statistical Analysis
In the 10-year period the total amount of 2,732 seed samples taken from 119 pedunculate oak FSOs were analysed by the LIS. However, data from the years in which the greatest number of FOs submitted seed samples were taken into consideration for this study. The period of 2009-2018 included: year 2010 (when 35 FOs submitted seed samples), year 2011 (32 FOs), year 2015 (29 FOs) and year 2017 (27 FOs). Furthermore, only data from FOs represented by at least two seed samples from a single FSO in all years with higher number of seed samples were additionally filtered. In such a way, data of 15 FOs with various numbers of seed samples per FSO (at least two) and from the four years were further processed.
Statistical analyses were conducted using RStudio ver. 1.2.5001 (RStudio Team 2019) and SAS/STAT 15.1 software (SAS Institute Inc. 2018). Descriptive analysis was performed using the MEANS procedure in SAS to calculate arithmetic means and standard deviations of the traits. Analysis of variance (ANOVA) was performed using the MIXED procedure in SAS, to establish statistical significance of analysed factors for the SV trait. Fixed effect of a seed stand i (i=1….15), random effect of a higher sample number years y (y=1…4), random effect of MC and random effect of acorn size (N·kg-1, being average number of acorns per kg) were the analysed factors. Pearson's correlation analyses were performed using the Hmisc package in R (Harrell et al. 2019) to determine significant associations between the mean SV and other traits (MC and N·kg-1). The correlation analyses were done with data combined for all seed stands as well as with a single stand data.
Data on MC, N·kg-1 and SV from 15 FOs were analysed. In them, FSOs were represented by at least 2 seed samples in each of the four higher sample number years (Table 2). The highest average estimates of MC were in 2015 and 2017 (MC = 41.1%). In 2015, MC ranged from 43.8% in FOs Otok and Gunja to 36.8% in FO Lekenik, while in 2017, it ranged from 44.1% in FO Nova Gradiška to 37.6% in FO Kutina. The lowest average MC was in 2011 (35.8%), ranging from a minimum of 33.1% (FO Vrbanja) to a maximum of 38.5% (FO Garešnica). The largest average N·kg-1 was in 2017 (189 acorns·kg-1), ranging from 221 acorns·kg-1 in FO Valpovo to 160 acorns·kg-1 in FO Nova Gradiška. In 2015, there were the smallest N·kg-1 (172 acorns·kg-1), ranging from 204 acorns·kg-1 in FO Sisak to 137 acorns·kg-1 in FO Kutina. On average, SV was the most consistent in 2010, when it ranged from a minimum of 74.3% in FO Nova Gradiška to a maximum of 88% in FO Daruvar. In 2011, SV was the most inconsistent, when it ranged from a minimum of 38.5% in FO Vrbanja to a maximum of 92.7% in FO Garešnica.
In general, there were no significant differences in SV among FOs or FSOs, i.e. the stand effect was not significant for this trait (Table 3). However, the years-within-stand effect was statistically significant indicating differences in the SV within FSOs across various years. Likewise, the seed-moisture effect and the acorn-size effect (both nested within a stand) were significant as well (Table 3).
Table 3. Factorial ANOVA summary for viability of Q. robur acorns (SV). Acorns from selected FSOs in 15 FOs were sampled in four mast years. Analysed factors were: fixed effect of a stand (levels: 1….15), random nested effects of: years-within-stand [Years(Stand)], acorn moisture-within-stand [Moist(Stand)] and acorn size-within-stand [Size(Stand)]. Significance of the factors is indicated by red colour (α=0.05).
SV from FSOs greatly varied among the years with higher sample number and these variations were observed in samples from all FSOs (Figure 1, showing these variations in just two FSOs).
Figure 1. SV distributions across the higher sample number years: (a) acorns from the FSO in Sisak and (b) acorns from the FSO in Nova Gradiška. The graphs show large variations in SV from the same FSO among years.
Correlation analyses revealed significant positive relationship between average SV and average MC (when combined all data; R=0.32, p<0.0001), but this correlation was even more pronounced when data were analysed separately by FSOs (Figure 2).
Figure 2. Correlation between mean SV and mean MC: (a) data from the FSO in Bjelovar and (b) data from the FSO in Valpovo.
Therefore, decreased SV in 2010, 2011 and 2015 may be explained by lower MC, at least partially. For example, FO Lekenik in 2015 had the lowest mean MC (36.8%) and low SV (59.6%). In the same year, the FO Gunja with the highest MC (43.8%) had highest SV, 76.3% (see Table 2).
Significant negative correlation was identified between average N·kg-1 and mean SV (when all data are combined, R=-0.22; p<0.0001). This relationship was even more pronounced when data were analysed separately by FSOs as well (Figure 3). In fact, this relationship revealed positive correlation between mean SV and its average size, because higher mean N·kg-1 means smaller average acorns size. For example, in 2015, there were on average 137 acorns per kg and 83.1% viable acorns from FO Kutina. On the contrary, FO Sisak was featured with a mean of 204 acorns per kg and 70.3% viable seeds (see Table 2).
Figure 3. Correlation between mean SV and average N·kg-1: (a) data from the FSO in Bjelovar and (b) data from the FSO in Garešnica.
Observations of seed yield in Quercus robur L. FSOs gathered during 10 years across Croatia revealed that there was no year of complete acorn absence. However, acorn yield showed considerable variations, both within and among years. Four times acorn crops were synchronized in all monitored FOs in the years 2010, 2011, 2015 and 2017 (Table 2). These results correspond to the general observations of cyclic acorn production, i.e. populations or individuals exhibited differences in a specific year, which resulted in variations in the annual acorn production (Goodrum et al. 1971, Cecich and Sullivan 1999, Healy et al. 1999, Greenberg 2000, Koenig and Knops 2002, Abrahamson and Layne 2003, Pearse et al. 2016, Bogdziewicz et al. 2018). For pedunculate oak, Gradečki-Poštenjak et al. (2011) reported significant crop year occurrence in regular intervals of every 2 to 3 years (5 mast years in a 11-year period), though quite different in quantity of crop yield. Although it is stated that the full yield follows the year in which the yield was absent or was very poor (Idžojtić 2013), our findings highlight that seed production in one year was followed sequentially by a high acorn crop in the next (in 2010 and 2011 we recorded consecutive acorn years). The results corroborate other authors who reported possible large seed crops in successive years (eg. Koenig et al. 1994). The successive high seed crops are possible also in other tree species (for example, Tapper (1992) noted an increased probability of fruiting in years following high seed production in Fraxinus excelsior and Norton and Kelly (1988) observed high seed production in successive years in Dacrydium cupressinum).
Despite the relatively large number of studies, there is limited knowledge about mechanisms and factors driving variable seed production. Allen et al. 2014 and Buechling et al. 2016 state that the initiation of masting results from a combination or sequence of climate cues. For Q. robur these include high spring and summer temperature within the crop years (Askeyev et al. 2005, Caignard et al. 2017, Hanley et al. 2019) and cool, wet conditions in the early autumn preceding the event (Crawley and Long 1995). In addition, masting variations within genus Quercus are highly site- and species-specific. For example, warm spring and summer conditions promoted increased acorn production in Q. lobata (Koenig et al. 2015), cool summer temperatures in Q. macrocarpa and warm spring temperatures 2 years prior to acorn maturation in Q. rubra (Koenig and Knops 2014). Summer drought, date of last spring frost and spring temperature were important for Q. velutina and Q. rubra, while for Q. alba spring temperature on days without rain was important (Sork et al. 1993). Consequently, there are many other factors that can influence masting besides just favourable environmental conditions. The idea of a combination of unfavourable environmental conditions (which limit reproduction), subsequent accumulation of resources (more resources spent on reproduction) and released resources for reproduction when environmental conditions are favourable is based on research conducted by Bogdziewicz et al. 2018. Also, potential factors which affect acorn crop are site and stand conditions, tree position and crown size (Dey 1995). The inherent periodicity may vary because of unfavourable temperature, precipitation in the time of flowering and the occurrence of stress caused by drought or frost periods during previous years (Harapin et al. 1996, Askeyev et al. 2005, Koenig et al. 2010). Some assumptions are the abundance of nutrients and substances required for the development of seeds, the synchronized flowering of most trees in a given locality and the lower adaptation ability of trees to pests (Sork et al. 1993, Kelly 1994). Different conclusions about the impact of factors affecting seed yield indicate the need for further research on this topic, drawing particular attention to crop quantification.
Seed quality is defined as “a measure of characteristics or attributes that will determine the performance of seeds when sown or stored” (Hampton 2002). Timing of collections can be a key factor in determining seed quality because maximum SV occur at physiological maturity (Bonner 2008). Collecting too early can results in lower seed quality due to seed immaturity, while collecting too late can also be detrimental, because seeds may be lost due to predation by animals or insects, or seed deterioration. Given the importance of acorn quality, the aim of this research was to test the effect of seed size and MC on SV. SV is an important parameter for plant conservation and research because it denotes the degree to which the seed is alive, metabolically active and whether it possesses enzymes capable of catalysing metabolic reactions needed for germination and seedling growth. In the current study, there were no significant differences in SV among FSOs (Table 3), but SV among years within FSOs were statistically significant (Figure 1). Additional support for this conclusion is provided by studies in which considerable variability in acorn seed viability (or germination) occurs between different sites (Pritchard and Manger 1990, Phillips 1992, Gradečki-Poštenjak et al. 2018, Gradečki-Poštenjak et al. 2011, Franjević et al. 2018).
Importance of collecting larger acorns is sometimes pointed out (Matić et al. 1996c, Crnković 2004), as there is a correlation between acorn size and the height in early phases of the plants’ life cycle (Kleinschmit 1993, Majer 2002, Quero et al. 2007, Landergott et al. 2012, Kesić et al. 2018). However, it is also generally accepted that larger seeds perform better than small seeds (Westoby et al. 1992). Kaliniewicz and Tylek (2018) found that the germination capacity of the smallest acorns ranged from 33% to 73%, while the largest acorns were characterized by the highest germination capacity in the range from 89% to 100%. Gradečki-Poštenjak et al. (2011) also reported a relationship between mean acorn size and mean acorn viability (yield 2006 – viability 83%, pcs·kg-1 185; yield 2010 – viability 71%, pcs·kg-1 203). Our research confirms these findings, i.e. lower mean number of acorns per kg correlated with higher viability (Figure 3). From this, it can be assumed that larger acorns indicate better quality, i.e. increased germination capacity. This assumption was confirmed for other tree species as well (e.g. for the Castanea sativa (Cicek and Tilki 2007)). Contrary, for some tree species germination characteristics were not significantly influenced by seed size and weight (e.g. for mountain hemlock (Edwards and El-Kassaby 1996) or Quercus libani (Alptekin and Tilki 2002)).
Acorns of the highest quality have MC of 40–45% fresh weight (Suszka et al. 2000, Szabla and Pabian 2009). Doody and O’Reilly (2008) reported that freshly harvested acorns had 46–48% of MC (about 24 h after harvesting). Özbingöl and O’reilly (2005) reported that acorn mean MC at delivery time was 42–43%, while Chmielarz et al. (2022) state that the mean MC of the acorns upon delivery was 37.7% and 40.8% of fresh weight for different seed lot. In our study, the mean MC of the acorns at delivery time was 39.6%, ranging from 33.1% to 44.1% (Table 2). These results were slightly lower than the previously reported research. The reasons for this were probably the storage conditions and time lag between the collection and transfer to the laboratory. MC of acorns at the time of shedding varies from 30% to 55% depending on the species (Bonner 1974b, Gosling 1989, Sobrino-Vesperinas and Viviani 2000, Joët et al. 2013), but it rapidly falls, which is primarily due to desiccation (Pritchard 1991, Gosling 1989, Connor and Sowa 2003). For example, in Q. coccifera and Q. pubescens viability was lost when MC dropped below 26% (Ganatsas and Tsakaldimi 2013), 15% in Q. nigra (Bonner 1996), and 22% in Q. alba (Connor et al. 1996). Earlier studies showed that the critical MC for pedunculate oak seeds was approximately 40%, below which viability declined rapidly (Suszka and Tylkowski 1980, Gosling 1989, Poulsen and Eriksen 1992). Suszka (2002) found that acorns dried to a MC below 22% did not germinate. Our results also clearly showed decreasing acorn SV due to lower MC (Figure 2). On average, viability drops below 70% when acorn mean moisture decrease below 36%.
The results of this study provide information on the seed yield from Quercus robur seed objects across Croatia in 10 years and the effects of seed size and seed moisture content on seed viability. Acorn production was very variable, with a considerable inter-annual variability in seed production and variability among seed objects within the same year. In the study period, four years were identified as years with higher number of samples. The results of testing seed viability showed significant variations among years within a forest seed object, but no difference in seed viability among seed objects. There were significant positive correlations between the impact of acorn size as well moisture content on seed viability.
AGM, SB2 and MI conceived the research; AGM and SB2 processed the data and performed statistical analysis; MI secured the research funding; MGP performed the verification of laboratory analysis; MI, ML, ZV, MGP and SB1 helped to draft the manuscript; AGM and SB2 wrote the manuscript.
This work has been supported in part by Croatian Science Foundation under the project IP-2018-01-8189 “Dynamic of fructification and conservation of genetic resources of pedunculate oak (Quercus robur L.) and european beech (Fagus sylvatica L.) in light of climate changes (CropForClim)".
We would like to thank Mladen Major and Ivanka Lacković for technical support in laboratory analyses.
Conflicts of Interest
The authors declare no conflict of interest.
Abideen MZ, Gopikumar K, Jamaludheen V, 1993. Effect of seed character and its nutrient content on vigour of seedlings in Pongamia pinnata and Tamarindas indica. My Forest 29: 225-230.
Abrahamson WG, Layne JN, 2003. Long-term patterns of acorn production for five oak species in xeric Florida uplands. Ecology 84(9): 2476-2492. https://doi.org/10.1890/01-0707.
Allen RB, Hurst JM, Portier J, Richardson SJ, 2014. Elevation-dependent responses of tree mast seeding to climate change over 45 years. Ecol Evol 4(18): 3525-3537. https://doi.org/10.1002/ece3.1210.
Alptekin CU, Tilki F, 2002. Effects of stratification and pericarp removal on germination of Quercus libani acorns. Silva Balcanica 2: 21-28.
Aniszewska M, Błuszkowska U, Zychowicz W, Brzózko J, 2020. Impact of mechanical treatment of pedunculate oak (Quercus robur L.) seeds on germination time and seedling quality. J Forest Res-JPN 25(6): 420-425. https://doi.org/10.1080/13416979.2020.1824630.
Askeyev OV, Tischin D, Sparks TH, Askeyev IV, 2005. The effect of climate on the phenology, acorn crop and radial increment of pedunculate oak (Quercus robur) in the middle Volga region, Tatarstan, Russia. Int J Biometeorol 49(4): 262-266. https://doi.org/10.1007/s00484-004-0233-3.
Bellari C, Tani A, 1993. Influence of time of collection on the viability of seeds of Alnus cordata. Ann Acad Ital Sci For 42: 259-285.
Bogdziewicz M, Steele MA, Marino S, Crone EE, 2018. Correlated seed failure as an environmental veto to synchronize reproduction of masting plants. New Phytol 219(1): 98-108. https://doi.org/10.1111/nph.15108.
Bonner FT, 1974a. Seed testing. In: Seeds of Woody Plants in the United States, Agriculture Handbook No. 450. For. Service, USDA, Washington D.C., USA.
Bonner FT, 1974b. Maturation of acorns of cherrybark, water, and willow oaks. Forest Sci 20(3): 238-242.
Bonner FT, 1996. Responses to drying of recalcitrant seeds of Quercus nigra L. Ann Bot-London 78(2): 181-187. https://doi.org/10.1006/anbo.1996.0111.
Bonner FT, 2008. The woody plant seed manual. United States Department of Agriculture, Forest Service, Agriculture Handbook 727. Available online: https://www.fs.fed.us/rm/pubs_series/wo/wo_ah727.pdf (4 January 2022).
Buechling A, Martin PH, Canham CD, Shepperd WD, Battaglia MA, 2016. Climate drivers of seed production in Picea engelmannii and response to warming temperatures in the southern Rocky Mountains. J Ecol 104(4): 1051-1062. https://doi.org/10.1111/1365-2745.12572.
Caignard T, Delzon S, Bodénès C, Dencausse B, Kremer A, 2019. Heritability and genetic architecture of reproduction-related traits in a temperate oak species. Tree Genet Genomes 15(1): 1-12. https://doi.org/10.1007/s11295-018-1309-2.
Caignard T, Kremer A, Firmat C, Nicolas M, Venner S, Delzon S, 2017. Increasing spring temperatures favor oak seed production in temperate areas. Sci Rep-UK 7: 1-8. https://doi.org/10.1038/s41598-017-09172-7.
Cecich RA, Sullivan NH, 1999. Influence of weather at time of pollination on acorn production of Quercus alba and Quercus velutina. Can J Forest Res 29(12): 1817-1823. https://doi.org/10.1139/x99-165.
Chmielarz P, Suszka J, Wawrzyniak MK, 2022. Desiccation does not increase frost resistance of pedunculate oak (Quercus robur L.) seeds. Ann Forest Sci 79 (3): 1-12. https://doi.org/10.1186/s13595-022-01121-3.
Cicek E, Tilki F, 2007. Seed size effects on germination, survival and seedling growth of Castanea sativa Mill. Journal of Biological Sciences 7(2): 438-441.
Connor KF, Bonner FT, Vozzo JA, 1996. Effects of desiccation on temperate recalcitrant seeds: Differential scanning calorimetry, gas chromatography, electron microscopy, and moisture studies on Quercus nigra and Quercus alba. Can J Forest Res 26(10): 1813-1821.
Connor KF, Sowa S, 2003. Effects of desiccation on the physiology and biochemistry of Quercus alba acorns. Tree Physiol 23(16): 1147-1152. https://doi.org/10.1093/treephys/23.16.1147.
Crawley MJ, Long CR, 1995. Alternate Bearing, Predator Satiation and Seedling Recruitment in Quercus robur L. J Ecol 83(4): 683-696. https://doi.org/10.2307/2261636.
Crnković S, 2004. Kvantitativne i kvalitativne osobine žira hrasta lužnjaka (Quercus robur L.) u sastojinama sliva rijeke Česme. Sumar list 128(7-8): 413-430.
Davidson RH, Edwards DGW, Sziklai O, El-Kassaby YA, 1996. Genetic variation in germination parameters among populations of Pacific silver fir. Silvae Genet 45(2-3): 165-171.
den Ouden J, Jansen PA, Smit R, 2005. Jays, Mice and Oaks: Predation and Dispersal of Quercus robur and Q. petraea in North-western Europe. In: Forget P-M, Lambert JE, Hulme PE, Vander Wall SB (eds) Seed Fate: Predation, dispersal, and seedling establishment. Wallingford, Oxfordshire, UK; Cambridge, MA : CABI Pub.
Devetaković JR, Nonić M, Prokić B, Šijačić-Nikolć M, Popović V, 2019. Acorn Size Influence on the Quality of Pedunculate Oak (Quercus robur L.) One-Year Old Seedlings. Reforesta 8: 17–24. https://doi.org/10.21750/REFOR.8.02.72.
Dey DC, 1995. Acorn production in red oak. Forest Research Information Paper, 127.
Doody CN, O’Reilly C, 2008. Drying and soaking pretreatments affect germination in pedunculate oak. Ann Forest Sci 65. https://doi.org/10.1051/forest:2008027.
Edwards DGW, El-Kassaby YA, 1996. The effect of stratification and artificial light on the germination of mountain hemlock seeds. Seed Sci Technol 24(2): 225-235.
Farmer REJ, 1980. Comparative analysis of first year growth on 6 deciduous tree species. Can J Forest Res 10: 35-41.
Forestry Commission, 2018. Guidance for Seed Testing at Forestry Commission Approved Forest Tree Seed Testing Facilities, Appendix 1. Available online: https://www.gov.uk/government/organisations/forestry-commission (1 May 2020).
Franjević M, Drvodelić D, Kolar A, Gradečki-Poštenjak M, Hrašovec B, 2018. Impact of oak lace bug Corythucha arcuata (Heteroptera: Tingidae) on pedunculate oak (Quercus robur) seed quality. Natural resources green technology & sustainable development-GREEN/3, 161-165.
Ganatsas P, Tsakaldimi M, 2013. A comparative study of desiccation responses of seeds of three drought-resistant Mediterranean oaks. Forest Ecol Manag 305: 189-194. https://doi.org/10.1016/j.foreco.2013.05.042.
Goodrum PD, Reid VH, Boyd CE, 1971. Acorn Yields, Characteristics, and Management Criteria of Oaks for Wildlife. J Wildlife Manage 35(3): 520-532. https://doi.org/10.2307/3799707.
Gosling PG, 1989. The effect of drying Quercus robur acorns to different moisture contents, followed by storage, either with or without imbibition. Forestry 62(1): 41-50. https://doi.org/10.1093/forestry/62.1.41.
Gradečki Poštenjak M, 2017. Ekološko klimatske promjena i problem obnove šuma hrasta lužnjaka u spačvanskom bazenu – SPAČVA, Poglavlje 8.2. Izvješće za OKFŠ HŠ 2013. – 2016.
Gradečki-Poštenjak M, Novak Agbaba S, Ćelepirović N, Posarić D, 2018. Qualitative properties of pedunculate oak acorns (Quercus robur L.) from Spačva basin and the consequences of its inadequate storage. Radovi (Hrvatski šumarski institut) 46(1): 1-13.
Gradečki-Poštenjak M, Novak-Agbaba S, Licht R, Posarić D, 2011. Dinamika plodonošenja i kvaliteta uroda sjemena hrasta lužnjaka (Quercus robur L.) u narušenim ekološkim uvjetima. Sumar list 135(13): 169-181.
Greenberg CH, 2000. Individual variation in acorn production by five species of southern Appalachian oaks. Forest Ecol Manag 132(2-3): 199-210. https://doi.org/10.1016/S0378-1127(99)00226-1.
Greenberg CH, Parresol BR, 2002. Dynamics of acorn production by five species of Southern Appalachian oaks. In: McShea, William J, Healy, William M (eds) Oak forest ecosystems: ecology and management for wildlife, Baltimore, Johns Hopkins University Press, 149-172.
Hampton JG, 2002. What is seed quality? Seed Sci Technol 30: 1-10.
Hanley ME, Cook BI, Fenner M, 2019. Climate variation, reproductive frequency and acorn yield in English Oaks. J Plant Ecol 12(3): 542-549. https://doi.org/10.1093/jpe/rty046.
Harapin M, Halambek M, Liović B, Novak Agbaba S, Matošević D, Sever S, 1996. Causes of the absence of acorn crop in Croatia during the period 1991–1995. In: Sever S (ed) Zaštita šuma i pridobivanje drva. Šumarski fakultet Zagreb, Šumarski institut Jastrebarsko, pp. 75-81.
Harmer R, 1994. Natural regeneration of broadleaved trees in Britain: II seed production and predation. Forestry 67(4): 275-286. https://doi.org/10.1093/forestry/67.4.275-a.
Harrell Jr FE, Dupont C, Many O, 2019. Hmisc: Harrell Miscellaneous. R package version 4.3-0. https://CRAN.R-project.org/package=Hmisc.
Healy WM, Lewis AM, Boose EF, 1999. Variation of red oak acorn production. Forest Ecol Manag 116(1-3): 1-11. https://doi.org/10.1016/S0378-1127(98)00460-5.
Idžojtić M, 2013. Dendrologija - Cvijet, Plod, Češer, Sjeme. Sveučilište u Zagrebu. Šumarski fakultet. Zagreb, Croatia, 479.
Isagi Y, Sugimura K, Sumida A, Ito H, 1997. How does masting happen and synchronize? J Theor Biol 187(2): 231-239.
Jayasankar S, Babu LC, Suclhakara K, Unnithan VKG, 1999. Provenance variation in seed and germination characteristics of teak (T. grandis L.F.). Seed Sci Technol 27: 131-139.
Joët T, Ourcival JM, Dussert S, 2013. Ecological significance of seed desiccation sensitivity in Quercus ilex. Ann Bot-London 111(4): 693-701. https://doi.org/10.1093/aob/mct025.
Kaliniewicz Z, Tylek P, 2018. Influence of scarification on the germination capacity of acorns harvested from uneven-aged stands of pedunculate oak (Quercus robur L.). Forests 9(3): 100. https://doi.org/10.3390/f9030100.
Kasprzyk I, Ortyl B, Dulska-Jeż A, 2014. Relationships among weather parameters, airborne pollen and seed crops of Fagus and Quercus in Poland. Agr Forest Meteorol 197: 111-122. https://doi.org/10.1016/j.agrformet.2014.05.015.
Kelly D, 1994. The evolutionary ecology of mast seeding. Trends Ecol Evol 9(12): 465-470. https://doi.org/10.1016/0169-5347(94)90310-7.
Kesić L, Stojnić S, Orlović S, Pavlović L, Lozjanin R, Tepavac A, Vaštag E, 2018. Varijabilnost morfoloških karaktera žira hrasta lužnjaka (Quercus robur L.), kitnjaka (Q. petraea (Matt.) Lieb.) i cera (Q. cerris L.). Topola 201/202: 187-201.
Kleinschmit J, 1993. Intraspecific variation of growth and adaptive traits in European oak species. Annales Des Sciences Forestières 50(Supplement): 166-185. https://doi.org/10.1051/forest:19930716.
Koenig WD, Knops JM, 2002. The behavioral ecology of masting in oaks. In: McShea WJ, Healy WM (eds) Oak forest ecosystems: ecology and management for wildlife. Baltimore, Johns Hopkins University Press, 129–148.
Koenig WD, Knops JMH, 2014. Environmental correlates of acorn production by four species of Minnesota oaks. Popul Ecol 56(1): 63-71. https://doi.org/10.1007/s10144-013-0408-z.
Koenig WD, Knops JMH, Carmen WJ, 2010. Testing the environmental prediction hypothesis for mast-seeding in California oaks. Can J Forest Res 40(11): 2115-2122.
Koenig WD, Knops JMH, Carmen WJ, Pearse IS, 2015. What drives masting? The phenological synchrony hypothesis. Ecology 96(1): 184-192. https://doi.org/10.1890/14-0819.1.
Koenig WD, Mumme RL, Carmen WJ, Stanback MT, 1994. Acorn production by oaks in central coastal California: Variation within and among years. Ecology 75(1): 99-109. https://doi.org/10.2307/1939386.
Landergott U, Gugerli F, Hoebee SE, Finkeldey R, Holderegger R, 2012. Effects of seed mass on seedling height and competition in European white oaks. Flora: Morphology, Distribution, Functional Ecology of Plants 207(10): 721-725. https://doi.org/10.1016/j.flora.2012.09.001.
Liebhold A, Sork V, Peltonen M, Koenig, W, Bjørnstad ON, Westfall R, Elkinton J, Knops JMH, 2004. Within-population spatial synchrony in mast seeding of North American oaks. Oikos 104(1): 156-164. https://doi.org/10.1111/j.0030-1299.2004.12722.x.
Majer S, 2002. Variability of Quercus robur L. and Quercus petraea (Matt.) Liebl. acorn size in the region of the Pomeranian plains. Dendrobiology 47(Supplement): 25-31.
Martiník A, Dobrovolný L, Palátová E, 2014. Tree growing space and acorn production of Quercus robur. Dendrobiology 71: 101-108. https://doi.org/10.12657/denbio.071.010.
Matić S, Komlenović N, Orlić S, Oršanić M, 1996c. Nursery production of pedunculated oak. In: Klepac D (ed) Hrast lužnjak u Hrvatskoj. Hrvatska akademija znanosti i umjetnosti, “Hrvatske šume” doo, Zagreb, Croatia, 423-425.
Matić S, Orlić S, Harapin M, 1996a. Sjeme hrasta lužnjaka kao temeljni uvjet nastanka i opstanka lužnjakovih šuma. In: Klepac D (ed) Hrast lužnjak (Quercus robur L.) u Hrvatskoj. Hrvatska akademija znanosti i umjetnosti, Centar za znanstveni rad u Vinkovcima i Hrvatske šume, Zagreb-Vinkovci, Croatia, 145-157.
Matić S, Oršanić M, Anić I, 1996b. Urod žira u prirodnim sastojinama hrasta lužnjaka u Hrvatskoj. In: Mayer B (ed) Unapređenje proizvodnje biomase šumskih ekosustva. Šumarski fakultet Sveučilišta u Zagrebu, Zagreb, Croatia, 105-111.
Nikolić N, Orlović S, Krstić B, Kevrešan Ž, 2006. Variability of acorn nutrient concentrations in pedunculate oak (Quercus robur L.) genotypes. Journal of Forest Science 52: 51-60. https://doi.org/10.17221/4487-jfs.
Norton DA, Kelly D, 1988. Mast seeding over 33 yearsby Dacrydium cupressinum Lamb. (rimu) (Podocarpaceae) in New Zealand: the importance of economies of scale. Funct Ecol 2: 399-408.
Official Gazette NN 75/09, 61/11, 56/13, 14/14, 32/19, 98/19. Zakon o šumskom reprodukcijskom materijalu. Available online: https://www.zakon.hr/z/597/Zakon-o-%C5%A1umskom-reprodukcijskom-materijalu.
Özbingöl N, O'reilly C, 2005. Increasing acorn moisture content followed by freezing-storage enhances germination in pedunculate oak. Forestry 78(1): 73-81. https://doi.org/10.1093/forestry/cpi007.
Pearse IS, Koenig WD, Kelly D, 2016. Mechanisms of mast seeding: resources, weather, cues, and selection. New Phytol 212(3): 546-562. https://doi.org/10.1111/nph.14114.
Pesendorfer MB, Bogdziewicz M, Szymkowiak J, Borowski Z, Kantorowicz W, Espelta JM, Fernández‐Martínez M, 2020. Investigating the relationship between climate, stand age, and temporal trends in masting behavior of European forest trees. Glob Change Biol 26(3): 1654-1667. https://doi.org/10.1111/gcb.14945.
Phillips R, 1992. Environmental factors contribute to acorn quality: Elevation, on- or off-tree collection influence the viability of blue oak acorns. Calif Agr 46(5): 30-32. https://doi.org/10.3733/ca.v046n05p30.
Poštenjak K, Gradečki M, 2001. Neki uzroci oštećenja i kakvoća sjemena lužnjaka (Quercus robur L.) i nizinskog brijesta (Ulmus minor Rich.) tijekom plodonošenja u ekološko-gospodarskim tipovima II-G-10 i II-G-20. In: Matić S, Krpan APB (eds) Znanost u potrajnom gospodarenju Hrvatskim šumama. Šumarski fakultet Sveučilišta u Zagrebu, Šumarski institut, Jastrebarsko, Zagreb, Croatia.
Poulsen KM, Eriksen EN, 1992. Physiological aspects of recalcitrance in embryonicaxes of Quercus robur L. Seed Sci Res 2(4):215–221.
Pritchard HW, 1991. Water potential and embryonic axis viability in recalcitrant seeds of Quercus rubra. Ann Bot-London 67(1): 43-49. https://doi.org/10.1093/oxfordjournals.aob.a088098.
Pritchard HW, Manger KR, 1990. Quantal Response of Fruit and Seed Germination Rate in Quercus robur L. and Castanea sativa Mill, to Constant Temperatures and Photon Dose. J Exp Bot 41(12): 1549-1557. https://doi.org/10.1093/jxb/41.12.1549.
Quero JL, Villar R, Marañón T, Zamora R, Poorter L, 2007. Seed-mass effects in four Mediterranean Quercus species (Fagaceae) growing in contrasting light environments. Am J Bot 94(11): 1795-1803. https://doi.org/10.3732/ajb.94.11.1795.
RStudio Team, 2019. RStudio: Integrated Development for R. RStudio, Inc., Boston, MA. Available at: http://www.rstudio.com/.
SAS Institute Inc. 2018. SAS/STAT® 15.1 User´s Guide. Cary, NC: SAS Institute Inc.
Sever K, Škvorc Ž, Krstonošić D, Ostrogović MZ, Franjić J, 2013. Which ecophysiological factors influence reproduction of forest trees and whether trees produced seed more frequantly and abundantly in the past? Radovi 45(2): 175–194.
Sobrino-Vesperinas E, Viviani AB, 2000. Pericarp micromorphology and dehydration characteristics of Quercus suber L. acorns. Seed Sci Res 10(3): 401-407. https://doi.org/10.1017/s0960258500000441.
Sork VL, Bramble J, Sexton O, 1993. Ecology of mast-fruiting in three species of North American deciduous oaks. Ecology 74(2): 528-541. https://doi.org/10.2307/1939313.
Suszka B, Muller C, Bonnet-Masimbert M, 2000. Nasiona leśnych drzew liściastych. Od zbioru do siewu. Seeds of deciduous forest trees. From harvest to sowing. Warszawa, Wydawnictwo Naukowe PWN.
Suszka B, Tylkowski T, 1980. Storage of acorns of the English oak (Quercus robur L.) over 1-5 winters. Arboretum Kórnickie 25: 199-229.
Suszka J, 2002. Improvement of methods of storage and pre-sowing treatmentseeds of English oak (Quercus robur L.) and European beech (Fagus sylvatica L.). Doctoral dissertation, Instiute of Dendrology Polish Academy of Sciences, Kórnik, Poland.
Szabla K, Pabian R, 2009. Szkółkarstwo kontenerowe: nowe technologie i techniki w szkółkarstwie leśnym. Container nursery: new technologies and techniques in forest nursery. 2nd ed. Warszawa, Centrum Informacji Lasów Państwowych.
Tapper PG, 1992. Irregular fruiting in Fraxinus excelsior. J Veg Sci 3(1): 41-46. https://doi.org/10.2307/3235996.
Toon PG, Haines RJ, Dieters MJ, 1990. Relationship between seed weight, germination and seedling-height growth in Pinus caribae, Morele. var. hondurensis barre and Golfri. Seed Sci Technol 19(2): 389-402.
Van der Meer PJ, Jorritsma ITM, Kramer K, 2002. Assessing climate change effects on long-term forest development: Adjusting growth, phenology, and seed production in a gap model. Forest Ecol Manag 162(1):39-52. https://doi.org/10.1016/S0378-1127(02)00049-X.
Wesołowski T, Rowiński P, Maziarz M, 2015. Interannual variation in tree seed production in a primeval temperate forest: does masting prevail? Eur J For Res 134: 99-112.
Westoby M, Jurado E, Leishman M, 1992. Comparative evolutionary ecology of seed size. Trends Ecol Evol 7(11): 368-372. https://doi.org/10.1016/0169-5347(92)90006-W.
Willan RL 1985. A Guide to Forest Feed Handling. FAO Forestry Paper. FAO, Rome, 20/2.
Worrell R, Nixon CJ, 1991. Factors affecting the natural regeneration of oak in upland Britain. Occasional Paper - Forestry Commission, 31.
© 2022 by the Croatian Forest Research Institute. This is an Open Access paper distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/4.0).