This study was conducted to evaluate the abundance and distribution pattern of three keystone Vachellia taxa in wadi Khoda and wadi Rahaba, Gebel Elba National Park, a protected area in south-eastern Egypt. These taxa included Vachellia tortilis subsp. tortilis, Vachellia tortilis subsp. raddiana, and Vachellia ehrenbergiana. In wadi Khoda, only two of these taxa were detected (V. tortilis subsp. raddiana and V. tortilis subsp. tortilis), while all three taxa were encountered in wadi Rahaba. The density of trees in wadi Khoda was 34.3 plant ha−1 compared to 26.3 plant ha−1 in wadi Rahaba. Vachellia tortilis subsp. raddiana was the most frequently observed tree, with an average of 47.93% and 68.25% in wadi Rahaba and wadi Khoda, respectively. Crown depth and tree height were mainly associated with elevation, indicating that elevation plays a key role in the growth of these Vachellia taxa. Our results suggest that human activities have had limited effect on the distribution of these three keystone taxa. Thus, management in Gebel Elba National Park should continue to limit the impact of human activities on these three keystone species.
The keystone species concept is an important aspect of population ecology, community ecology, and conservation biology1,2, and its application is likely to be critical with ongoing climate change3. Keystone species can be identified because they have a larger effect on communities and ecosystems than would be predicted based on their abundance or dominance. Loss of keystone species within communities and ecosystems is likely to result in secondary extinction events, and in extreme cases these events can lead to community and ecosystem collapse4. The critical importance of keystone species is derived from the wide range of biotic interactions they engage in with other community members (predation, competition, herbivory, mutualism, facilitation, etc.) and their influence on abiotic environmental conditions2. Keystone species have been described in a range of ecosystems (e.g., marine, fresh water, terrestrial, etc.) and have included a variety of taxa (e.g., fungi, animals, and plants)1,3,5.
Plant communities consisting of isolated or scattered trees occur across the globe, and such trees have been described as keystone species, or “keystone structures”6. This certainly applies to trees and shrubs that are members of plant communities in arid and semi-arid habitat7. Many members of Acacia s.l. (Fabaceae: Mimosoideae8), which are broadly distributed around the world, are considered keystone species within the communities they reside. For example, they are considered keystone species in parts of Australia9, Pakistan10, the Kalahari Desert, Botswana11, Tunisia12,13,14, the Sinai Desert, Egypt15,16, and south-eastern Egypt16,17. As pointed out by Abdallah et al.12, isolated trees in arid habitats, including Vachellia species., have several characteristics that contribute to their keystone status: (1) shade from their canopies prevents extreme temperature fluctuations, increases soil moisture levels, and provides shelter for wildlife, (2) they improve soil conditions through biological nitrogen fixation and litter fall by increasing soil nitrogen content, organic carbon, and water-holding capacity, (3) they increase plant and animal biodiversity as a consequence of characteristics one and two, (4) they provide a source of food for wildlife, and (5) they provide a source of fuel, fodder, and medicines for local people and their domesticated animals. Because of their critical importance, a full characterization of keystone species and the roles they play within communities and ecosystems is urgently needed; especially as they are adversely impacted by various human activities.
The Gebel Elba mountain range is an extension of the Afromontane “biodiversity hotspot” and is at the northern limit of the Eritreo-Arabian province and the Sahel regional transition zone18. The relatively high abundance of moisture of this mountain range leads to higher plant biodiversity than reported elsewhere in Egypt, it consists of 458 species, which constitutes approximately 21% of the Egyptian flora19,20. According to the plant checklist provided by Boulos21, the flora of Egypt consists of 2100 taxa belonging to 755 genera and 129 families; including 45 genera and 228 taxa in the Fabaceae. Gebel Elba is one of the seven main phytogeographical regions in Egypt21. Additionally, the region’s tree and shrub species diversity is higher than in any other regions in Egypt19, with some Sahelian woody elements restricted to the Gebel Elba region and not reported elsewhere in Egypt. Of the 10 Vachellia (synonym: Acacia8) species reported in Egypt, seven are known to occur in the Gebel Elba region, with Vachellia asak (synonym: Acacia asak) and Vachellia oerfota subsp. oerfota (synonym: Acacia oerfota subsp. oerfota) restricted to this region.
An analysis of the plant communities of wadi Yahmib and three of its tributaries, on the north-western slopes of Gebel Elba, revealed the presence of seven plant communities, with these communities being arrayed across an elevational (environmental) gradient17. The Vachellia tortilis subsp. tortilis (synonym: Acacia tortilis subsp. tortilis) community was the main vegetation type on Gebel Elba. This community type occurred commonly in the water channels of wadis and gravel terraces from low to mid elevations (130–383 m), and the species was a member of all of the other six communities in the study area17. In addition, Vachellia tortilis subsp. raddiana (synonym: Acacia tortilis subsp. raddiana) was an overstory co-dominant species in another community on Gebel Elba. Finally, a third acacia species, Vachellia etbaica (synonym: Acacia etbaica), was also detected in this study.
Within arid and semi-arid ecosystems across north Africa and the Arabian Peninsula, plant ecologists have focused their attention on describing the vegetation of wadis that drain to the Red Sea, with these studies focusing on keystone Vachellia species12,13,14,15,16,17,22,23. The present study aimed to contribute to this body of knowledge by determining the distribution, abundance, and describing the growth characteristics of three Vachellia tree taxa in wadi Khoda and wadi Rahaba, in Gebel Elba National Park, south-eastern Egypt. These data will allow us to provide detailed descriptions of the characteristics of these three taxa. This study is essential at this moment because these tree taxa are keystone species within these ecosystems, and their presence and conservation are likely to be threatened by human activities and ongoing climate change.
Materials and methods
The Gebel Elba National Park (35° 00′ E–37° 00′ E, 22° 00′ N–23° 50′ N) is located in the southeastern corner of Egypt and comprises an area of approximately 35,600 km2 (Fig. 1). The boundaries of this protected area extend more than 50 km north of Shalatein, Egypt, eastward to the Red Sea, south to the border with Sudan, and westward into the Eastern Desert24.
This study was undertaken in 2017 and 2018. Over these two years, the average daily air temperature ranged between 25 and 29 °C, the maximum air temperatures were 40.8 °C in 2017 and 41.9 °C in 2018, the minimum air temperatures were 15.3 °C in 2017 and 14.3 °C in 2018. Annual precipitation was 31.1 mm in 2017 and 17.6 mm in 2018 (Fig. 2). Mean daily relative humidity ranged between 39 and 45% in 2017 and 38 and 44% in 2018, with a range of 28% to 61% relative humidity across the two years.
Three Vachellia tree taxa; Vachellia tortilis subsp. tortilis, Vachellia tortilis subsp. raddiana, and Vachellia ehrenbergiana (synonym: Acacia ehrenbergiana) were the focus of this study because they are the only tree taxa present at the two study sites (there was no other woody vegetation). During each year of the study, a transect was established along the length of wadi Khoda and wadi Rahaba, in Gebel Elba National Park. We chose these two areas for this study because these three Vachellia tree taxa are common in these wadis (Fig. 3). The transect in wadi Rahaba had a north to south-east orientation and the transect in wadi Khoda had a west to east orientation. The direction of the transect in each wadi was determined by the direction of the wadi’s drainage system. A total of 30 macroplots (200 m × 100 m) were established in the two wadis (Rahaba, n = 23; Khoda, n = 7), with distances of approximately 3 km between each macroplot (Figs. 1, 4).
For each macroplot, all tree taxa were identified according to Boulos19. Because this study was conducted during a period of drought, saplings and seedlings were only rarely observed in the two wadis. Consequently, we only encountered mature trees with a DBH > 10 cm in the macroplots we sampled. The tree characteristic parameters we measured included crown depth, crown diameter, crown volume, tree height, Diameter at Breast Height, DBH (tree diameter), tree radius, and the basal area of each tree25. The crown-to height ratio (C/H ratio) was calculated by dividing the crown volume by tree height. Crown diameter was measured by projecting several edges of the crown to the ground and measuring the length along an axis that extended from crown edge to crown edge. The crown diameter can be used to estimate the area of a tree’s crown (which is used in the crown surface area and volume calculations) by obtaining the average of two axes26. In this study, the diameters of two axes perpendicular to each other (N–S and E–W) were measured and averaged. Crown depth was measured as the distance between the top of the tree and the base of the crown. The base of the crown was identified by the lowest complete whorl of branches or the lowest single branch that formed the canopy of a tree. Crown depth was expressed as the "crown length ratio", which is calculated as the crown length divided by the tree height. Crown volume (Cv) was estimated from crown diameter (D) and crown depth (L) using the equation described by West26:
The trees in each wadi were numbered sequentially, and their latitude/longitude coordinates were recorded using a 12XL Garmin GPS unit. The nearest-neighbor distance for each pair of trees was measured and recorded. As noted by Cottam and Curtis27, many of these nearest-neighbor distance values are duplicates, since paired neighbors which have each other as nearest neighbors make up a large portion of the total dataset.
To determine the distribution pattern of the three Vachellia tree taxa we detected in this study, we used the method of Clark and Evans28. Briefly, in a population of N individuals with known density (d) and distance from each nearest-neighbor pair (r), the mean observed distance is calculated as follows:
The mean distance that would be expected if members of a population were randomly distributed (re) is calculated as:
The degree to which the observed distribution for the distance to the nearest neighbor approaches or departs from random expectation was expressed as the ratio (R) as follows:
According to Clark and Evans28 and Petrere29, R has a defined range: 0.0 < R < 2.1491. If R = 0.0, individuals are highly aggregated, when R = 2.1491, there is a completely uniform distribution pattern, and when R = 1.0, the distribution pattern of individuals is random.
Parametric statistical tests were performed on key variables after checking for normality and equality of variance. One-way analysis of variance (ANOVA) was used to evaluate statistical differences among the parameters used to characterize the three Vachellia tree taxa at wadi Rahaba. With only two tree taxa detected at wadi Khoda, t-tests were used to analyze significance among the mean values of these parameters. All statistical analyses were carried out using JMP (ver 4. SAS Institute, Cary, NC, USA).
The elevation of macroplots were significantly different (P < 0.0001), and the elevation of macroplots increased with distance from the Red Sea (Fig. 4). For wadi Khoda, the macroplot with the lowest elevation was located 29 m above sea level and the macroplot at the highest elevation was 224 m. For wadi Rahada, the elevation of the macroplots ranged from 11 to 418 m above sea level.
Tree abundance, distribution, and density
All three Vachellia tree taxa were found in wadi Rahaba, while only two of these taxa (V. tortilis subsp. raddiana and V. tortilis subsp. tortilis) were observed in wadi Khoda. In wadi Khoda, seven trees, on average, were found in each macroplot (with density of 34.3 trees ha−1); these seven individuals consisting of, on average, five V. tortilis subsp. raddiana trees and two V. tortilis subsp. tortilis trees. There was an average of 5.26 trees per plot in wadi Rahaba, with a density of 26.3 trees ha−1 (even though no trees were observed in three of the macroplots in wadi Rahaba). Vachellia tortilis subsp. raddiana was the most frequently detected Vachellia tree taxa detected in the two wadis we analyzed (Table 1), it represented 68.75% of the trees at wadi Khoda and 47.93% of the trees at wadi Rahaba. Vachellia tortilis subsp. tortilis was the second-most common tree at both study sites (42.15% of the trees at wadi Rahaba and 31.25% of the trees at wadi Khoda). Only twelve V. ehrenbergiana trees were observed within the wadi Rahaba microplots (9.92% of the trees at this wadi) (Table 1).
Variation in tree characteristic parameters
Values for these tree characteristic parameters varied among the three Vachellia tree taxa and between the two wadis where this study was conducted (Fig. 5). A comparison of V. tortilis subsp. raddiana and A. tortilis subsp. tortilis in the two wadis did not reveal significant differences between the two taxa for crown diameter and tree height (Fig. 5). However, these two Vachellia trees exhibited significantly higher values for crown depth, crown volume, DBH, tree radius, basal area, and C/H ratio in wadi Khoda.
In wadi Khoda, were only two Vachellia tree taxa were detected (V. tortilis subsp. raddiana and V. tortilis subsp. tortilis), V. tortilis subsp. raddiana had significantly higher values for crown depth (d.f. = 1; t-test 5.021; P < 0.0001), crown diameter (d.f. = 1; t-test 4.064; P = 0.0002), crown volume (d.f. = 1; t-test 3.419; P = 0.0013), tree height (d.f. = 1; t-test 6.402; P < 0.0001), and C/H ratio (d.f. = 1; t-test 2.868; P < 0.0063) compared to V. tortilis subsp. tortilis. There were no significant differences for DBH, tree radius, and basal area for these two species at wadi Khoda (Fig. 5).
In wadi Rahaba, three Vachellia tree taxa were encountered, and they had significant differences for the growth characteristics measured in this study. Vachellia tortilis subsp. raddiana had significantly greater values compared to V. tortilis subsp. tortilis and V. ehrenbergiana for crown depth (F = 40.00; P < 0.0001), crown diameter (F = 41.38; P < 0.0001), crown volume (F = 22.17; P < 0.0001), tree height (F = 71.22; P < 0.0001), and C/H ratio (F = 17.20; P < 0.0001). Whereas, V. tortilis subsp. raddiana and V. ehrenbergiana had greater values than V. tortilis subsp. tortilis for DBH (F = 11.97; P < 0.0001), tree radius (F = 11.97; P < 0.0001), and basal area (F = 4.48; P < 0.0085) (Fig. 5).
Correlation coefficients of elevation with all tree characteristic parameters, as well as the correlation among tree characteristics were provided in Fig. 6. These results showed that crown depth and tree height are significantly associated with elevation (r = 0.44 and 0.48, respectively), while elevation was not significantly correlated with other tree characteristic parameters (see Fig. 6). Crown diameter, crown volume, DBH, and tress radius showed significantly positive correlation patterns. On the other hand, crown depth and tree height were significantly correlated with each other and other traits, but not basal area (Fig. 6).
Mean observed nearest neighbor distance
The mean observed nearest neighbor distance (r0) was 60.1 ± 6.2 m in wadi Khoda macroplots, compared to 61.6 ± 6.8 m in wadi Rahaba plots (Table 2). The mean expected distance (re) was shorter in the wadi Khoda macroplots (29.0 ± 2.7 m), compared with the value of re for trees in the wadi Rahaba macroplots (34.8 ± 2.6 m) (t-test, P < 0.05; Table 2). R values indicated that the distribution pattern of Vachellia tree taxa varied between random and completely uniform in both wadis. The R values were 1.6 and 1.7 in wadi Rahba and wadi Khoda, respectively (Table 2), and these values were significantly different (t-test, P < 0.05).
Variation between and among plant populations arises due to differences in genetic diversity, heterogeneity of resource availability, competition, herbivory, and pathogen attack, all of which effect the growth rates of individuals in a population30. Topographic and edaphic factors, especially altitude, play a pivotal role in the distribution of plant communities. Understanding the relationships between vegetation cover and these environmental factors contributes to developing sustainable management strategies for such communities31,32.
Results of this study showed clear differences in populations of three Vachellia tree taxi in two wadis in Gebel Elba National Park, wadi Khoda and wadi Rahaba. Two Vachellia tree taxa were recorded in wadi Khoda (V. tortilis subsp. raddiana and V. tortilis subsp. tortilis), whereas all three taxa were detected at wadi Rahaba (V. tortilis subsp. raddiana, V. tortilis subsp. tortilis, and V. ehrenbergiana). Although V. tortilis subsp. raddiana was the most frequently encountered taxa in both wadis, V. tortilis subsp. tortilis predominated in low elevation macroplots, with its frequency decreasing with increasing elevation (i.e., distance from the Red Sea). These findings suggest that the distribution and abundance of the three Vachellia taxa in these wadis is likely influenced by topography and elevation. In addition, soil properties, especially soil salinity, may play a role in the distribution and abundance of these taxa. Thus, the findings of the current study concerning the diversity of the three Vachellia taxa documented in these two wadis and the distribution of these taxa along a broad elevation gradient are in general agreement with similar studies conducted in south-eastern Egypt16,17,22, and elsewhere across the distribution of Vachellia species12,13,14,15,23.
Previous studies have reported that the growth rates of individual trees were influenced by internal tree competitiveness as well as, limited resources, such as sunlight and water availability33,34. For instance, the mean mass of seven-year old Acacia auriculiformis trees decreased with increasing stand density35. Alternatively, a few studies have reported that tree seedlings planted at high density exhibited more rapid growth rates than seedlings planted at low density36. However, the positive-growth responses associated with high density was found to be a short-lived phenomenon.
Henskens et al.37 reported that mean tree mass (and other tree growth parameters) increased with decreasing stand density. This occurred due the following factors: (1) increased competition for sunlight among individuals in high-density stands, as the leaves of the same tree and among trees overlap, which results in a decrease photosynthetic capacity, (2) with increasing stand density, the number and length of lateral branches gradually decreases, especially in the middle and lower parts of a tree, and the shape of the crown changes38, and (3) with increasing stand density, branch angles (the angle between the stem of a tree and its main lateral branches) decrease. Alcorn et al.39 reported that trees with greater branch angles have more open crowns, and greater effective leaf area for photosynthesis.
Surprisingly, the relationship between low-density tree stands and greater tree growth values was not observed in the current study. Trees in the high-density stands at wadi Khoda had greater values for crown depth, crown volume, DBH, tree radius, basal area, and C/H ratio, compared to the trees in the low-density stands at wadi Rahaba (Fig. 5). Vachellia trees growing in these two wadis did not exhibit significant differences in crown diameter and tree height. These results suggest that trees growing in these high-density stands were not engaging in intra- and interspecific competition, which often results in lower values for tree growth parameters, as reported in previous studies37. Instead, these results suggest that the higher density of trees at wadi Khoda may lead to positive biotic interactions, such as facilitation7,40, which would result in the greater tree growth values described here. Alternatively, the greater tree growth values of the Vachellia taxa at wadi Khoda may be due to differences in abiotic environmental conditions at the two study sites. For instance, the transect in wadi Khoda had a west to east orientation and the transect in wadi Rahaba had a north to south-east orientation (Fig. 1). Differences in the orientation of these two transects may have resulted in higher soil moisture content at wadi Khoda and led to the greater tree growth values we report. Additional research will be required to determine the relative role of biotic and abiotic factors in the growth of the three keystone Vachellia tree taxa in our study area.
The spatial distribution of the Vachellia tree taxa in both wadis revealed similar spacing among these trees (Table 2). The mean nearest neighbor distance (r0) was slightly shorter for the trees in wadi Khoda, but these differences were not statistically significant (P > 0.05). This result occurs because the Vachellia tree taxa in both wadis we studied have a scattered distribution, compared the denser stand of trees that typically occur in riparian zones, in which water availability is higher throughout much of the year. This pattern is consistent with that described by Ramsay41, concerning the distribution of trees in forests in Darfur, Sudan. The degree to which the observed tree distribution patterns either approach or depart from random expectation (R) were slighter greater than 1.5, indicating the random distribution of individual trees in both wadis28. This result occurs because the mean observed distance values (r0) were relatively close to the mean expected distance values (re) in both wadis. As pointed out by Cottam and Curtis27, this result can be a product of this type of paired nearest-neighbor analysis because many of the nearest neighbor values included in this dataset are duplicates. However, we also believe these results indicate that the distribution of Vachellia tree taxa at wadi Khoda and wadi Rahba is not being influenced by human activities.
The density of Vachellia taxa was higher in wadi Khoda, compared to wadi Rahaba. While V. tortilis subsp. raddiana was the most frequently encountered taxa in both wadis, V. tortilis subsp. tortilis predominated at lower elevations, with its frequency decreasing with increasing elevation. These results constitute the first step in confirming the keystone status of the three taxa in this region. The next steps in this determination would involve assessing the biotic interactions these taxa engage in with other community members, and their influence on abiotic environmental conditions. The random distribution pattern of the Vachellia trees in the two wadis suggests that human activities have had limited effect on their distribution. Management recommendations and practices in Gelba Elba National Park should continue to limit the impact of human activities. Finally, the data reported here serves as a baseline for future assessments of the status of these three keystone tree taxa, in this arid ecosystem.
Mills, L. S. et al. The keystone-species concept in ecology and conservation. Bioscience 43, 219–224 (1993).
Mouquet, N. et al. Extending the concept of keystone species to communities and ecosystems. Ecol. Lett. 16, 1–8. https://doi.org/10.1111/ele.12014 (2013).
Bond, W. J. Keystone species. In Biodiversity and Ecosystem Function. Praktische Zahnmedizin Odonto-Stomatologie Pratique Practical Dental Medicine (Geology) Vol. 99 (eds Schulze, E. D. & Mooney, H. A.) (Springer, Berlin, 1994). https://doi.org/10.1007/978-3-642-58001-7_11.
Christianou, M. & Ebenman, B. Keystone species and vulnerable species in ecological communities: strong and weak interactors?. J. Theor. Biol. 235, 95–103 (2005).
Power, M. E. et al. Challenges in the quest for keystones. Bioscience 46, 609–620 (1996).
Manning, A. D. et al. Scattered trees are keystone structures—implications for conservation. Biol. Conserv. 132, 311–321 (2006).
Pugnaire, F. I. et al. Facilitation between higher plant species in a semiarid environment. Ecology 77, 1420–1426 (1996).
Kyalangalilwa, B. et al. Phylogenetic position and revised classification of Acacia s.l. (Fabaceae: Mimosoideae) in Africa, including new combinations in Vachellia and Senegalia. Bot. J. Linn. Soc. 172, 500–523. https://doi.org/10.1111/boj.12047 (2013).
Crisp, M. D. & Lang, R. T. Age structure, distribution and survival under grazing of the arid-zone shrub Acacia burkittii. Oikos 27, 86–92 (1976).
Mahmood, S. et al. Spatial pattern of variation in populations of Acacia nilotica in semi-arid environment. Int. J. Environ. Sci. Technol. 2, 193–199 (2005).
Steenkamp, C. J. et al. Age determination of Acacia erioloba trees in the Kalahari. J. Arid Environ. 72, 302–313 (2008).
Abdallah, F. et al. The influence of Acacia tortilis (Forssk.) subsp. raddiana (Savi) and livestock grazing on grass species composition, yield and soil nutrients in arid environments of South Tunisia. Flora 203, 116–125 (2008).
Noumi, Z. & Chaieb, M. Dynamics of Acacia tortilis (Forssk.) Hayne subsp. raddiana (Savi) Brenan in arid zone of Tunisia. Acta Botanica Gallica Bot. Lett. 159, 121–126 (2012).
van Coillie, F. et al. Monotemporal assessment of the population structure of Acacia tortilis (Forssk.) Hayne ssp. raddiana (Savi) Brenan in Bou Hedma National Park, Tunisia: a terrestrial and remote sensing approach. J. Arid Environ. 129, 80–92. https://doi.org/10.1016/j.jaridenv.2016.02.009 (2016).
Abd El-Wahab, R. H. et al. Anthropogenic effects on population structure of Acacia tortilis subsp. raddiana along a gradient of water availability in South Sinai, Egypt. Afr. J. Ecol. 52, 308–317. https://doi.org/10.1111/aje.12121 (2013).
El-Azazi, E. et al. Ecological studies of some Acacia species grown in Egyptian deserts. Glob. J. Biosci. Biotechnol. 2, 485–492 (2013).
Abutaha, M. M. et al. Plant communities and their environmental drivers on an arid mountain, Gebel Elba, Egypt. Veg. Classif. Surv. 1, 21–36 (2020).
White, F. The vegetation of Africa: a descriptive memoir to accompany the Unesco/AETFAT/UNSO vegetation map of Africa. 356 pp (UNESCO, Paris, France, 1983).
Boulos, L. Flora and vegetation of the deserts of Egypt. Flora Mediterr. 18, 341–359 (2008).
Zahran, M. A. & Willis, A. J. The Vegetation of Egypt 2nd edn, 437 (Springer, Dordrecht, 2009). https://doi.org/10.1007/978-1-4020-8756-1.
Boulos, L. Flora of Egypt Checklist (Revised Annotated Edition) 410 (Al-Hadara Publishing, Cairo, 2009).
AbdElRahman, H. F. & Evans, K. Environmental effects on morphology of Acacia tortilis group in the Red Sea Hills, north-eastern Sudan and south-eastern Egypt. For. Ecol. Manag. 255, 254–263 (2008).
Noumi, Z. et al. The effects of browsing on the structure of Acacia tortilis (Forssk.) Hayne spp. raddiana (Savi) Brenan along a gradient of water availability in arid zone of Tunisia. J. Arid Environ. 74, 625–631 (2010).
Al-Gohary, I. H. Phytogeographical analysis of the vegetation of eleven wadis in Gebel Elba, Egypt. Int. J. Agric. Biol. 10, 161–166 (2008).
Addo-Fordjour, P. et al. Liana species richness, abundance and relationship with trees in the Bobiri forest reserve, Ghana: impact of management systems. For. Ecol. Manag. 257, 1822–1828 (2009).
West, P. W. Tree and Forest Measurement (Springer, New York, 2009).
Cottam, G. & Curtis, J. T. The use of distance measures in phytosociological sampling. Ecology 37, 451–460 (1956).
Clark, P. J. & Evans, F. C. Distance to nearest neighbor as a measure of spatial relationships in populations. Ecology 35, 445–453 (1954).
Petrere, M. J. The variance of the index (R) of aggregation of Clark and Evans. Oecologia 68, 158–159 (1985).
Weiner, J. Size hierarchies in experimental populations of annual plants. Ecology 66, 746–752 (1985).
Zhang, Z. et al. Effects of topographical and edaphic factors on the distribution of plant communities in two subtropical karst forests, southwestern China. J. Mt. Sci. 10, 95–104. https://doi.org/10.1007/s11629-013-2429-7 (2013).
Abbas, A. M. et al. Floristic diversity and phytogeography of Jabal Fayfa: a subtropical dry zone, south-west Saudi Arabia. Diversity 12, 345. https://doi.org/10.3390/d12090345 (2020).
Weiskittel, A. R. et al. Forest Growth and Yield Modeling (Wiley, Hoboken, 2011).
Aakala, T. et al. Influence of competition and age on tree growth in structurally complex old growth forests in Northern Minnesota, USA. For. Ecol. Manag. 308, 128–135 (2013).
Feng, H. & Xue, L. Competition-density effect of tree organs in Acacia auriculiformis stands. J. For. Res. Jpn. 30, 891–898 (2019).
Woodruff, D. R. et al. Effects of stand density on the growth of young Douglas-fir trees. Can. J. For. Res. 32, 420–427 (2002).
Henskens, F. L. et al. Physiological basis of spacing effects on tree growth and form in Eucalyptus globules. Trees 15, 365–377 (2001).
Baldwin, V. C. Jr. et al. The effects of spacing and thinning on stand and tree characteristics of 38-year-old Loblolly Pine. For. Ecol. Manag. 137, 91–102 (2000).
Alcorn, P. J. et al. Effects of initial planting density on branch development in 4-year-old plantation grown Eucalyptus pilularis and Eucalyptus cloeziana trees. For. Ecol. Manag. 252, 41–51 (2007).
Brooker, R. W. et al. Facilitation in plant communities: the past, the present, and the future. J. Ecol. 96, 18–34 (2008).
Ramsay, D. M. The forest ecology of central Darfur. Sudan Gov.. For. Bull. 1, 1–80 (1958).
The authors extend their appreciation to the Dean of Scientific Research at King Khalid University for funding this work through General Research Project under Grant Number G.R.P-91-41. We would like to thank Sameh Kotb Abd-Elmabod, Soils and Water Use Department, Agricultural and Biological Research Division, National Research Centre (NRC), Dokki, Egypt, for preparing the map of the study area.
The authors declare no competing interests.
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Abbas, A.M., Al-Kahtani, M., Novak, S.J. et al. Abundance, distribution, and growth characteristics of three keystone Vachellia trees in Gebel Elba National Park, south-eastern Egypt. Sci Rep 11, 1284 (2021). https://doi.org/10.1038/s41598-020-79542-1
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