
Figure 1
Geographic location of the study area. The upper left panel shows the location of Vietnam's Central Highlands Region (pink colour); the lower left panel shows the location of the study area (light green colour) and the right panel shows the vegetation cover of tropical dry dipterocarp forests (fluorescent green colour) and the distribution of sampled plots for the four different dry forest (DF) types.

Figure 2
Tree species-area curve between species richness and the 103 main plots that were sampled within a total of 10.3 ha of natural forest in Vietnam's Central Highlands Region.

Figure 3
Species richness (number of species per plot); stem density (number of individual stems per plot); family richness (number of families per plot); basal area (sum of basal area per plot); mean diameter (mean diameter per plot); mean height (mean height per plot) for the four dry forest (DF) types studied.

Figure 4
Relationship between species relative importance and species rank in abundance for the top 5 tree species recorded in the four dry forest (DF) types studied.
Table 1
Similarity Index (J’) matrix between four dry forest (DF) types in Vietnam's Central Highlands Region.
| Forest types | DFR | DFM | DFP | DFV |
|---|---|---|---|---|
| DFR | 45.76% | 43.10% | 36.11% | |
| DFM | 59.09% | 53.85% | ||
| DFP | 58.11% | |||
| DFV |

Figure 5
Top ten tree species and their contribution based on their importance value index (IVI), in terms of relative basal area (RBA), relative density (RD) and relative frequency (RF) for the four dry forest (DF) types studied in Vietnam's Central Highlands Region.
Table 2
Consolidated details of tree diversity in four types of tropical dry dipterocarp forests in Vietnam's Central Highland Region.
| Forest types | Margalef's Index (R) | Shannon-Wiener diversity (H’) | Simpson Index (D) | Evenness Index (E) |
|---|---|---|---|---|
| DFR | 8.43±1.03a | 2.29±0.16a | 0.87±0.02a | 0.32±0.02a |
| DFM | 5.90 ±1.62b | 1.85±0.38b | 0.78±0.12b | 0.34±0.04a |
| DFP | 5.44±1.80b | 1.80±0.32b | 0.77±0.08b | 0.35±0.07a |
| DFV | 5.88±2.00b | 1.81±0.37b | 0.76±0.11b | 0.34±0.06a |
| Kruskal-Wallis chi-squared | 10.553 | 10.572 | 9.9064 | 1.4935 |
| p-value | 0.0144 | 0.01428 | 0.01938 | 0.6838 |

Figure 6
Frequency (%) of trees according to different DBH classes for the four dry forest (DF) types studied. Notes: DFR: rich dry forest; DFM: medium dry forest; DFP: poor dry forest; DFV: very poor dry forest.

Figure 7
Regeneration status for the top 10 tree species recorded in the four dry forest (DF) types studied. Notes: DFR: rich dry forest; DFM: medium dry forest; DFP: poor dry forest; DFV: very poor dry forest.
Supplementary Table S1
Nationally rare and IUCN red list of threatened species recorded in four different dry forest (DF) types of Vietnam's Central Highlands.
| Species name | IUCN | DFR | DFM | DFP | DFV |
|---|---|---|---|---|---|
| Dalbergia oliveri Gamble ex Prain | EN | - | - | - | 1 |
| Hopea recopei Pierre ex Laness | EN | - | 1 | - | - |
| Dipterocarpus intricatus Dyer | EN | - | - | - | 1 |
| Pterocarpus macrocarpus Kurz. | EN | - | 1 | 3 | 12 |
| Dalbergia bariensis Pierre | EN | 5 | 2 | 21 | 41 |
| Sindora siamensis Teysm. | LR | - | 1 | - | - |
| Dipterocarpus tuberculatus Roxb. | NT | 8 | 157 | 250 | 376 |
| Dipterocarpus obtusifolius Teijsm. | NT | 7 | 158 | 242 | 323 |
| Shorea obtusa Wall. | NT | - | 15 | 15 | 37 |
| Vitex ajugaeflora Dop | VU | - | 2 | 1 | 33 |
| Dalbergia tonkinensis Prain | VU | - | - | - | 1 |
| Parashorea stellata Kurz | VU | - | 1 | - | - |
| Dipterocarpus alatus Roxb. | VU | - | 24 | 1 | 5 |
| Hopea odorata Roxb. | VU | - | - | - | 2 |
| Shorea roxburghii G. Don | VU | 26 | 85 | 309 | 448 |
[i] Notes: IUCN: International Union for Conservation of Nature; EN: endangered species; LR: species at lower risk; NT: near threatened species; VU: vulnerable species.
Supplementary Table S2
List of species richness found in four different dry forest (DF) types of Vietnam's Central Highlands. Tree species are ranked from the highest to the lowest based on their importance value index (IVI).
| DFR | DFM | DFP | DFV | ||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
| No | Species | IVI | No | Species | IVI | No | Species | IVI | No | Species | IVI |
| 1 | Shorea siamensis | 52.1 | 1 | Dipterocarpus tuberculatus | 37.8 | 1 | Shorea obtusa | 52.2 | 1 | Shorea obtusa | 40.8 |
| 2 | Shorea obtusa | 42.8 | 2 | Dipterocarpus obtusifolius | 37.4 | 2 | Dipterocarpus tuberculatus | 41.6 | 2 | Dipterocarpus tuberculatus | 37.8 |
| 3 | Xylia xylocarpa | 35.6 | 3 | Shorea obtusa | 36.3 | 3 | Dipterocarpus obtusifolius | 40.9 | 3 | Dipterocarpus obtusifolius | 32.7 |
| 4 | Terminalia alata | 32.6 | 4 | Xylia xylocarpa | 19.1 | 4 | Terminalia alata | 22.6 | 4 | Shorea siamensis | 23.1 |
| 5 | Dillenia sp. | 15.2 | 5 | Shorea siamensis | 18.1 | 5 | Terminalia chebula | 17.8 | 5 | Aporosa villosa | 14.8 |
| 6 | Dipterocarpus tuberculatus | 13.1 | 6 | Terminalia alata | 15.6 | 6 | Shorea siamensis | 14.1 | 6 | Xylia xylocarpa | 13.8 |
| 7 | Aporosa villosa | 11.6 | 7 | Aporosa villosa | 11.2 | 7 | Aporosa villosa | 12.1 | 7 | Terminalia alata | 11.5 |
| 8 | Dipterocarpus obtusifolius | 8.6 | 8 | Dipterocarpus alatus | 10.2 | 8 | Xylia xylocarpa | 10.1 | 8 | Terminalia chebula | 10.2 |
| 9 | Elaeocarpus hygrophilus | 7.3 | 9 | Irvingia malayana | 8.8 | 9 | Dillenia sp. | 6.8 | 9 | Morinda citrifolia | 9.9 |
| 10 | Syzygium cumini | 6.3 | 10 | Dillenia sp. | 7.4 | 10 | Neonauclea purpurea | 6.1 | 10 | Dalbergia bariensis | 6.8 |
| 11 | Dalbergia bariensis | 6.3 | 11 | Terminalia chebula | 7.1 | 11 | Dalbergia bariensis | 5.8 | 11 | Albizia lebbeck | 6.3 |
| 12 | Haldina cordiflora | 5.3 | 12 | Lagerstroemia calyculata | 6.6 | 12 | Strychnos nux–blanda | 5.1 | 12 | Dillenia sp. | 5.9 |
| 13 | Cratoxylon formosum | 4.9 | 13 | Lagerstroemia speciosa | 6.5 | 13 | Shorea roxburghii | 4.3 | 13 | Shorea roxburghii | 5.6 |
| 14 | Barringtonia acutangula | 4.8 | 14 | Terminalia corticosa | 5.6 | 14 | Morinda citrifolia | 4.3 | 14 | Syzygium cumini | 4.6 |
| 15 | Lagerstroemia speciosa | 4.6 | 15 | Shorea roxburghii | 5.6 | 15 | Lagerstroemia calyculata | 3.5 | 15 | Neonauclea purpurea | 4.5 |
| 16 | Schrebera swietenioides | 4.5 | 16 | Morinda citrifolia | 5.0 | 16 | Spondias pinnata | 3.4 | 16 | Lannea coromandelica | 4.2 |
| 17 | Neonauclea purpurea | 4.1 | 17 | Melia azedarach | 4.2 | 17 | Barringtonia acutangula | 3.3 | 17 | Cratoxylon formosum | 4.1 |
| 18 | Terminalia corticosa | 3.5 | 18 | Syzygium cumini | 4.1 | 18 | Cratoxylon formosum | 2.9 | 18 | Vitex ajugaeflora | 4.0 |
| 19 | Lagerstroemia calyculata | 3.3 | 19 | Spondias pinnata | 3.9 | 19 | Bombax ceiba | 2.9 | 19 | Barringtonia acutangula | 3.9 |
| 20 | Peristrophe bivalvis | 3.3 | 20 | Elaeocarpus hygrophilus | 3.9 | 20 | Semecarpus sp. | 2.8 | 20 | Strychnos nux–blanda | 3.2 |
| 21 | Shorea roxburghii | 3.2 | 21 | Cratoxylon formosum | 3.4 | 21 | Bauhinia malabarica | 2.3 | 21 | Melanorrhoea laccifera | 3.1 |
| 22 | Bauhinia malabarica | 3.1 | 22 | Neonauclea purpurea | 3.4 | 22 | Syzygium cumini | 1.9 | 22 | Castanopsis piriformis | 3.1 |
| 23 | Strychnos nux–blanda | 3.0 | 23 | Grewia nervosa | 2.9 | 23 | Anogeissus acuminata | 1.9 | 23 | Semecarpus sp. | 2.5 |
| 24 | Melia azedarach | 2.6 | 24 | Millingtonnia hortensis | 2.7 | 24 | Terminalia corticosa | 1.8 | 24 | Careya aborea | 2.4 |
| 25 | Diospyros maritima | 2.5 | 25 | Bombax ceiba | 2.6 | 25 | Grewia nervosa | 1.8 | 25 | Terminalia corticosa | 2.3 |
| 26 | Morinda citrifolia | 2.5 | 26 | Albizia lebbeck | 2.5 | 26 | Schrebera swietenioides | 1.8 | 26 | Spondias pinnata | 2.2 |
| 27 | Prunus arborea | 2.4 | 27 | Strychnos nux–blanda | 2.1 | 27 | Azadirachta indica | 1.8 | 27 | Pterocarpus macrocarpus | 2.1 |
| 28 | Artocarpus lakoocha | 2.3 | 28 | Peristrophe bivalvis | 2.0 | 28 | Pterocarpus macrocarpus | 1.7 | 28 | Bridelia balansae | 1.9 |
| 29 | Terminalia catappa | 2.2 | 29 | Semecarpus sp. | 1.8 | 29 | Engelhardtia chrysolepis | 1.6 | 29 | Prunus arborea | 1.9 |
| 30 | Castanopsis piriformis | 2.1 | 30 | Clausena excavata | 1.5 | 30 | Fructus Gleditschia | 1.6 | 30 | Grewia nervosa | 1.7 |
| 31 | Peltophorum pterocarpum | 2.1 | 31 | Vitex ajugaeflora | 1.5 | 31 | Phyllanthus emblica | 1.6 | 31 | Peristrophe bivalvis | 1.6 |
| 32 | Briedenia cambodiana | 2.0 | 32 | Barringtonia acutangula | 1.4 | 32 | Ficus | 1.4 | 32 | Bauhinia malabarica | 1.5 |
| 33 | Schrebera swietenioides | 1.4 | 33 | Lagerstroemia speciosa | 1.4 | 33 | Irvingia malayana | 1.5 | |||
| 34 | Dalbergia bariensis | 1.2 | 34 | Elaeocarpus hygrophilus | 1.3 | 34 | Catunaregam tomentosa | 1.4 | |||
| 35 | Parinari annamense | 1.1 | 35 | Albizia lebbeck | 1.1 | 35 | Lagerstroemia calyculata | 1.4 | |||
| 36 | Anogeissus acuminata | 0.9 | 36 | Catunaregam tomentosa | 1.1 | 36 | Bombax ceiba | 1.3 | |||
| 37 | Pterocarpus macrocarpus | 0.9 | 37 | Millingtonnia hortensis | 1.0 | 37 | Canthium horridum | 1.3 | |||
| 38 | Prunus arborea | 0.9 | 38 | Lannea coromandelica | 1.0 | 38 | Lagerstroemia speciosa | 1.3 | |||
| 39 | Parashorea stellata | 0.9 | 39 | Prunus arborea | 1.0 | 39 | Elaeocarpus hygrophilus | 1.2 | |||
| 40 | Hopea recopei | 0.8 | 40 | Canthium horridum | 1.0 | 40 | Anogeissus Acuminata | 1.1 | |||
| 41 | Engelhardtia roxburghiana | 0.8 | 41 | Rhamnus crenatus | 0.8 | 41 | Terminalia catappa | 1.0 | |||
| 42 | Neonauclea sessilifolia | 0.8 | 42 | Machilus odoratissima | 0.7 | 42 | Phyllanthus emblica | 0.9 | |||
| 43 | Peltophorum pterocarpum | 0.8 | 43 | Diospyros ehretioides | 0.6 | 43 | Quercus kerrii | 0.9 | |||
| 44 | Rhamnus crenatus | 0.7 | 44 | Vitex ajugaeflora | 0.6 | 44 | Senna siamea | 0.9 | |||
| 45 | Elaeocacpus macroceras | 0.7 | 45 | Briedenia cambodiana | 0.6 | 45 | Cratoxylon prunifolium | 0.9 | |||
| 46 | Stereospermum cylindricum | 0.7 | 46 | Buchanania latifolia | 0.6 | 46 | Garcinia oblongifolia | 0.8 | |||
| 47 | Bauhinia malabarica | 0.7 | 47 | Dipterocarpus alatus | 0.6 | 47 | Terminalia triptera | 0.7 | |||
| 48 | Machilus odoratissima | 0.7 | 48 | Mallotus philippinensis | 0.6 | 48 | Wrightia pubescens | 0.7 | |||
| 49 | Diospyros maritima | 0.7 | 49 | Terminalia calamansanai | 0.5 | 49 | Stereospermum cylindricum | 0.7 | |||
| 50 | Knema lenta | 0.6 | 50 | Terminalia catappa | 0.5 | 50 | Haldina cordiflora | 0.6 | |||
| 51 | Canarium subulatum | 0.6 | 51 | Peristrophe bivalvis | 0.5 | 51 | Rhamnus crenatus | 0.6 | |||
| 52 | Fructus Gleditschia | 0.6 | 52 | Polyalthia cerasoides | 0.5 | 52 | Parinari annamense | 0.6 | |||
| 53 | Lannea coromandelica | 0.6 | 53 | Terminalia calamansanai | 0.6 | ||||||
| 54 | Sindora siamensis | 0.6 | 54 | Dipterocarpus alatus | 0.5 | ||||||
| 55 | Hopea odorata | 0.5 | |||||||||
| 56 | Clausena excavata | 0.5 | |||||||||
| 57 | Azadirachta indica | 0.5 | |||||||||
| 58 | Ficus superba | 0.5 | |||||||||
| 59 | Mallotus philippinensis | 0.4 | |||||||||
| 60 | Millingtonnia hortensis | 0.4 | |||||||||
| 61 | Schefflera heptaphylla | 0.3 | |||||||||
| 62 | Litsea cambodiana | 0.3 | |||||||||
| 63 | Fructus Gleditschia | 0.3 | |||||||||
| 64 | Dalbergia tonkinensis | 0.3 | |||||||||
| 65 | Mangifera sp. | 0.3 | |||||||||
| 66 | Dalbergia oliveri | 0.3 | |||||||||
Supplementary Table S3
Structure, composition, and diversity of tree species in tropical dry forests of the present and previous studies.
| ID | Study area | Sampled area (ha) | Minimal DBH (cm) | Number of species | Number of families | Stand density | Stand basal area | Shannon-Weiner | Simpson | Evenness | Margalef's | Seedling (individuals / ha) | Sapling (individuals / ha) |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| 1 | Dadeldhura district, Western Nepal (Bhatta & Devkota, 2020) | 1.05 | >5 | 42 | 20 | 3162.9±194.3 | 13.77±0.88 | 15905±927.3 | 1876.2±143.4 | ||||
| 2 | 3 provinces from Central Highlands of Vietnam (Do et al., 2017) | 6.00 | >10 | 157 | 622 | 2.06 | 0.80 | ||||||
| 3 | Huai Kha Khaeng Wildlife Sanctuary, Thailand (Wanthongchai et al., 2014) | 0.75 | >4.5 | 54 | 667–1558 | 12.9–23.6 | 13000–40000 | 573–4570 | |||||
| 4 | Fasiakhali Wildlife Sanctuary, Bangladesh (Das et al., 2018) | 3.2 | >11 | 32 | 19 | 249 | 46.17 | 2.05 | 0.75 | ||||
| 5 | Eastern Ghats, Southern India (Gopalakrishna et al., 2015) | 7.9 | >10 | 128 | 45 | 994 | 5.1±3.6 | 1.1–3.5 | 0.4–1.0 | 0.5–0.9 | |||
| 6 | The North-Western Coast of Costa Rica (Hilje et al., 2015) | 0.9 | >5 | 96 | 41 | ||||||||
| 7 | YokDon National Park, Vietnam (Nguyen & Baker, 2016) | 2.8 | >1 | 38 | 1229 ±523 | 19.12 ±5.89 | 13383 | ||||||
| 8 | The Minas Gerais, Brazil (Calvo-Rodriguez et al., 2017) | 1.8 | >5 | 59 | 19 | 510–1091 | 3.13–25.34 | 0.9–1.3 | |||||
| 9 | Central America (Gillespie et al., 2000) | 0.7 | >2.5 | 204 | 58 | 1350–2650 | 17.7–25 | ||||||
| 10 | Guanacaste Province, Costa Rica (Hubbell, 1979) | 13.44 | >2 | 135 | |||||||||
| 11 | Sri Lanka (Karthigesu et al., 2019) | 0.12 | >5 | 446–1500 | 11.4–44.8 | 0.6–0.9 | 694–3400 | 773–4475 | |||||
| 12 | The North West Region of Cameroon (Sainge et al., 2020) | 12.3 | >10 | 178 | 42 | 157–404 | 6.8–32.4 | 2.7–3.5 | |||||
| 13 | Michoacán, Mexico (Méndez-Toribio et al., 2014) | 0.36 | >1 | 78 | 24 | 700–5600 | 9–44 | 0.41–3.5 | 0.04–0.71 | ||||
| 14 | Bandipur, South India (Suresh et al., 2016) | >1 | 66 | 2.46 | 0.81 | ||||||||
| 15 | The Accra Plains in South-East Ghana (Swaine et al., 1990) | 0.49 | >10 | 16 | 1332 | ||||||||
| 16 | Northern Sri Lanka (Thirukkumaran et al., 2017) | 0.12 | >5 | 32 | 18 | 446 | 1.54–2.29 | 0.86–0.94 | |||||
| 17 | Vindhyan Highlands, India (Chaturvedi & Raghubanshi, 2014) | 20 | >10 | 52 | 126–490 | 3.1–18 | 1.5–2.5 | 1.7–3.7 | 5040–14167 | 540–1383 | |||
| 18 | Minas Gerais, Southeastern Brazil (Coelho et al., 2012) | 0.3 | >5 | 50 | 21 | 1076–1226 | 17.8–29.3 | 1.52–2.58 | 0.48–0.64 |