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. 2023 Jan 11;18(1):e0279491. doi: 10.1371/journal.pone.0279491

First evidence of a monodominant (Englerodendron, Amherstieae, Detarioideae, Leguminosae) tropical moist forest from the early Miocene (21.73 Ma) of Ethiopia

Aaron D Pan 1,2,*,#, Bonnie F Jacobs 3,#, Rosemary T Bush 4,, Manuel de la Estrella 5,, Friðgeir Grímsson 6,#, Patrick S Herendeen 7,#, Xander M van der Burgt 8,, Ellen D Currano 9,#
Editor: Gongle Shi10
PMCID: PMC9833558  PMID: 36630378

Abstract

Many tropical wet forests are species-rich and have relatively even species frequency distributions. But, dominance by a single canopy species can also occur in tropical wet climates and can remain stable for centuries. These are uncommon globally, with the African wet tropics supporting more such communities than the Neotropics or Southeast Asia. Differences in regional evolutionary histories are implied by biogeography: most of Africa’s monodominance-forming species are Amherstieae-tribe legumes; monodominance in Neotropical forests occur among diverse taxonomic groups, often legumes, but rarely Amherstieae, and monodominance in Southeast Asian forests occurs mostly among Dipterocarpaceae species. African monodominant forests have been characterized ecologically and taxonomically, but their deep-time history is unknown despite their significant presence and bottom-up ecological influence on diversity. Herein we describe fossil leaflets of Englerodendron mulugetanum sp. nov., an extinct species of the extant genus Englerodendron (Berlinia Clade, Amherstieae, Detarioideae) from the 21.73 Ma Mush Valley site in Ethiopia. We also document a detailed study of associated legume pollen, which originate from a single taxon sharing characters with more than one extant descendant. Taxonomically, the pollen is most comparable to that from some extant Englerodendron species and supports a likely affiliation with the Englerodendron macrofossils. The Mush Valley site provides the first fossil evidence of a monodominant tropical forest in Africa as represented by leaflets and pollen. Previous studies documented >2400 leaves and leaflets from localities at six stratigraphic levels spanning 50,000–60,000 years of nearly continuous deposition within seven meters of section; all but the basal level contain ≥ 50% E. mulugetanum leaflets. Modern leaf litter studies in African mixed vs. monodominant forests indicates the likelihood of monodominance in the forests that surrounded the Mush paleolake, particularly after the basal level. Thus, we provide an early case for monodominance within the Amherstieae legumes in Africa.

Introduction

Modern moist and wet primary tropical forest formations are typically characterized by high to extremely high levels of biodiversity and can boast as many as 300 tree species within a single hectare [1, 2]. More unusual are natural moist and wet tropical forest formations that are dominated by a single tree species, often making up from 50% to nearly 100% of the canopy trees [3, 4]. While this phenomenon can be found in the tropics of Africa, the New World, and Asia, there are clear biogeographic differences among the three tropical regions, in part caused by the occurrence of monodominant species in at least 24 families and 51 genera. The majority of monodominant forests in the Neotropics and Africa are composed of species in the legume family (Leguminosae), but compared with Africa and Asia, Neotropical monodominant-forming forest taxa are more diverse; this is true whether considering all families or the diversity of subfamilies and tribes among legume dominants (Table 1) [3, 57]. African monodominant tropical forests are nearly always characterized by legume species in the tribe Amherstieae of the subfamily Detarioideae, many of which occur in the monophyletic and African endemic Berlinia Clade (Table 1) [8, 9]. A number of genera and species (even those not forming monodominant forest formations) within the Berlinia Clade have a tendency to form monotypic stands or are noted as often becoming gregarious where found [10]–thus, this African clade may have a propensity for forest ecological dominance. Tropical Asia is well-known and unique for the importance and Neogene diversity of the Dipterocarpaceae, and its monodominant forests are composed of species primarily in this family (Table 1) [11, 12].

Table 1. Monodominant tropical forests of the world and their dominant species component.

MONODOMINANT TROPICAL FOREST SPECIES HIGHER TAXONOMIC RANKINGS CONTINENT CITATION
Aucoumea klaineana Burseraceae AFRICA [66]
Terminalia superba Combretaceae AFRICA [66]
Aphanocalyx microphyllus Leguminosae: Detarioideae: Amherstieae AFRICA [61]
Brachystegia laurentii Leguminosae: Detarioideae: Amherstieae AFRICA [5]
Cynometra alexandri Leguminosae: Detarioideae: Amherstieae AFRICA [5]
Mbau (Gilbertiodendron dewevrei) forest Gilbertiodendron dewevrei Leguminosae: Detarioideae: Amherstieae AFRICA [5, 6]
Julbernardia seretii Julbernardia seretii Leguminosae: Detarioideae: Amherstieae AFRICA [5]
Microberlinia bisulcata Leguminosae: Detarioideae: Amherstieae AFRICA [62]
Talbotiella gentii Leguminosae: Detarioideae: Amherstieae AFRICA [92]
Tetraberlinia bifoliolata Leguminosae: Detarioideae: Amherstieae AFRICA [62]
Tetraberlinia korupensis Leguminosae: Detarioideae: Amherstieae AFRICA [62]
Tetraberlinia tubmaniana Leguminosae: Detarioideae: Amherstieae AFRICA [93]
Gilletiodendron glandulosum Leguminosae: Detarioideae: Detarieae AFRICA [68]
Musanga cecropioides Urticaceae AFRICA [94]
Kapur forest Dryobalanops aromatica Dipterocarpaceae ASIA (Malesia) [95]
Parashorea malaanonan Dipterocarpaceae ASIA (Malesia) [96]
Shorea albida Dipterocarpaceae ASIA (Malesia) [97]
Shorea curtisii Dipterocarpaceae ASIA (Malesia) [98]
Ulin forest Eusideroxylon zwageri Lauraceae ASIA (Malesia) [99]
Palaquium gutta Sapotaceae ASIA (Malesia) [100]
Dimorphocalyx glabellus Euphorbiaceae ASIA (South Asia: India) [101]
Strychnos nux-vomica Loganiaceae ASIA (South Asia: India) [101]
Tricalysia sphaerocarpa Rubiaceae ASIA (South Asia: India) [101]
Sal forest Shorea robusta Dipterocarpaceae ASIA (South Asia: India-Bangladesh) [102]
Hopea ferrera Dipterocarpaceae ASIA (Southeast Asia: NE Thailand) [103]
Backhousia bancroftii Myrtaceae AUSTRALIA [104]
Celaenodendron mexicanum Euphorbiaceae MESOAMERICA [105]
Quercus oleoides Fagaceae MESOAMERICA [106]
Pisonia grandis Nyctaginaceae OCEANIA (Micronesia) [107]
Ōhi’a forest Metrosideros polymorpha Myrtaceae OCEANIA (Polynesia: Hawaii) [108]
Oxandra polyandra Annonaceae SOUTH AMERICA [2]
Astrocaryum macrocalyx Arecaceae: Arecoideae: Cocoseae SOUTH AMERICA [2]
Astrocaryum murumuru Arecaceae: Arecoideae: Cocoseae SOUTH AMERICA [2]
Attalea speciosa Arecaceae: Arecoideae: Cocoseae SOUTH AMERICA [2]
Euterpe oleracea Arecaceae: Arecoideae: Euterpeae SOUTH AMERICA [109]
Mauritia flexuosa Arecaceae: Calamoideae: Lepidocaryeae SOUTH AMERICA [2]
Jacaranda densicoma Bignoniaceae SOUTH AMERICA [2, 110]
Tabebuia aurea Bignoniaceae SOUTH AMERICA [2]
Micrandra glabra Euphorbiaceae SOUTH AMERICA [2]
Mora gonggrijpii Leguminosae: Caesalpinoideae SOUTH AMERICA [2]
Mora oleifera Leguminosae: Caesalpinoideae SOUTH AMERICA [2]
Tachigali vaupesiana Leguminosae: Caesalpinoideae SOUTH AMERICA [2]
Mora excelsa Leguminosae: Caesalpinoideae: Dimorphandra Group A SOUTH AMERICA [2]
Dicymbe corymbosa Leguminosae: Detarioideae: Amherstieae SOUTH AMERICA [111]
Eperua falcata Leguminosae: Detarioideae: Detarieae SOUTH AMERICA [2]
Jauacaná caatinga forest Eperua leucantha Leguminosae: Detarioideae: Detarieae SOUTH AMERICA [2]
Caatinga Forest (Jebarú) Eperua purpurea Leguminosae: Detarioideae: Detarieae SOUTH AMERICA [2]
Peltogyne gracilipes Leguminosae: Detarioideae: Detarieae SOUTH AMERICA [112]
cativales’ Prioria copaifera Leguminosae: Detarioideae: Detarieae SOUTH AMERICA [113]
Machaerium hirtum Leguminosae: Faboideae: Dalbergieae SOUTH AMERICA [2]
Spirotropis longifolia Leguminosae: Faboideae: Ormosieae SOUTH AMERICA [114]
Pentacletha macroloba Leguminosae: Mimosoideae: SOUTH AMERICA [115]
Vitex cymosa Lamiaceae SOUTH AMERICA [2]
Igapó forest (black-water flooded forests) Eschweilera tenuifolia Lecythidaceae SOUTH AMERICA [116]
Lueheopsis hoehnei Malvaceae sensu lato SOUTH AMERICA [2]
Pachira nitida Malvaceae sensu lato SOUTH AMERICA [2]
Brosimum rubescens Moraceae SOUTH AMERICA [2]
Phyllanthus elsiae Phyllanthaceae SOUTH AMERICA [2]
Triplaris weigeltiana Polygonaceae SOUTH AMERICA [2]
Ruizterania retusa Vochysiaceae SOUTH AMERICA [2]

In addition to its biogeographic distinctiveness, Africa is unique among tropical regions with regard to the large areal extent of moist and wet monodominant forests [7, 13], which collectively occupy thousands of km2 [5, 1416]. They can be found in the Congo Basin to Cameroon and Nigeria and are dominated by, for example, Gilbertiodendron dewevrei (De Wild.) J.Léonard, 1952, Julbernardia seretii (De Wild.) Troupin, 1950, and Brachystegia laurentii (De Wild.) Louis ex J.Léonard, 1952 [5, 1416]. A number of causal mechanisms and species traits have been called upon to explain why in some circumstances monodominance emerges and then can persist for centuries. These include deep leaf litter and slow litter decomposition, large seed size, nutrient-poor soils, the presence of ectomycorrhizal symbionts, competitive advantages among the dominant taxa, and both shade and sun tolerance [4, 1719]. Detarioideae legumes have a long evolutionary history in Africa and the Neotropics dating to the early Cenozoic [20, 21], one might expect monodominance to have occurred in the deep past, perhaps even in South America where this phenomenon is relatively rare today. None has been identified to date, leaving undocumented the origins and biogeographic history of monodominant tropical wet forests.

In this paper, we describe an early Miocene taxon from Ethiopia (formerly referred to as “Legume 1” [22, 23]) and assign it to the Berlinia Clade. Previous work on the paleoecology of the locality that produced the new taxon found strong support for a forest community dominated by legume taxa overall, noting the relative abundance of “Legume 1” in particular, which comprises 1289 specimens (53%) of all leaves collected and documented (2427). Its long-term abundance through seven vertical meters of sampling prompted us to take a closer look at the structural nature of the forest community represented by all the fossil leaf assemblages to determine if monodominance is or is not represented at this locality, with the keystone role played by a Berlinia Clade taxon as happens in Africa today. We also looked at the dispersed pollen flora from the same sediments as the macrofossils to explore if Berlinia clade pollen occurs in the Mush record and if similar “monodominant” signals are reflected by the palynoflora.

Materials and methods

The Mush Valley fossil site is located in a region of the northwestern plateau of Ethiopia approximately 160 km northeast of Addis Ababa and between the towns of Debre Birhan and Debre Sina (9°47’N, 39°39’ E) [2225]. Abundant and diverse fossils including plants (leaf, wood, fruit, and seed compressions and pollen), vertebrates (rare mammals, anurans, and teleost fish compressions), and insect compressions are preserved in layers of lacustrine carbonaceous shale interbedded with thin layers of volcanic ash < ~3 cm thick [2327]; one exceptional interbedded ash horizon (fossil-bearing Level C) is 10 cm thick. The fossiliferous shales are constrained in age by 206Pb/238U dates on zircons within two volcanic ashes, one that is stratigraphically immediately below them and one five additional meters below that. These yield the following ages for the upper and lower ashes, respectively: 21.733 ± 0.060 Ma and 21.736 ± 0.015 Ma [28].

Research, particularly field work and the collection and analysis of fossil plants and geologic specimens from the Upper and Lower Mush Valley, Amhara, Ethiopia, was permitted by the Authority for Research and Conservation of Cultural Heritage (ARCCH), a governmental agency within the Ministry of Culture of Ethiopia. The necessary permits for multiple years of field work (2010–2013) resulting in the collection of the specimens referred to in this paper are on file at the national offices of the ARCCH in Addis Ababa, with copies to the regional office located in Debre Berhan. Preparation and description of fossils were permitted by the National Museum of Ethiopia, Addis Ababa, where the specimens are housed permanently. The project members complied with all relevant regulations. Additional information regarding the ethical, cultural, and scientific considerations specific to inclusivity in global research is included in S1 File.

Fossil leaves and leaflets were quarried from benches excavated such that a 5 cm thick shale unit could be removed in large blocks. To retard desiccation and specimen damage, the blocks were wrapped and transported in trunks to the National Museum of Ethiopia after each field season and left to dry during intervals of about six months at a time. Subsequent splitting, preparation, photography, and classification took place at the museum for all leaves or leaflets having ≥ 50% of the lamina preserved. Small, ~0.5 cm2, cuticle samples were removed from leaves to aid in classification. Cuticle preparations and microscope slides from herbarium samples are housed in the Roy M. Huffington Department of Earth Sciences at Southern Methodist University, Dallas, TX, USA [2325]. A total of 2427 leaves were classified (using morphotype names if not identified to taxon) from collections among two to three quarries at each of six stratigraphic levels (A-F) spanning 7 m of section [23]. A total of 49 morphotypes were classified, including “Legume 1”, the most common taxon described and named in this paper (see also, [22]). Inventories of morphotype descriptions and number of specimens per quarry and level are provided in Currano et al. [23] (main text and supplemental materials). Frequency distributions, diversity measures, and isotopic measurements were analyzed to evaluate paleoecology and to identify any patterns of variation within and between stratigraphic levels, thus gaining a spatial and temporal view of plant community characteristics [22, 23, 27]. The estimated time represented by these shale deposits is approximately one to three centuries per 5 cm-thick quarry collection, and approximately 50–60 kyrs in total, on the basis of comparison with dated Holocene and Pleistocene lake cores [23].

Fossil specimens were compared to extant Leguminosae specimens from herbaria housed at the United States National Museum of Natural History (US), Missouri Botanical Garden (MO), Botanical Research Institute of Texas (BRIT), and, via high resolution digital images from the Muséum national d’Histoire naturelle (MNHN) and Global Plants on JSTOR (S2 File). Additional comparisons were based on published material (citations in RESULTS). Methods for preparation of herbarium and fossil leaflet cuticle and venation are provided in Herendeen & Dilcher [29] and Pan et al. [25], respectively. Herbarium leaf cuticle slides are housed at the Chicago Botanic Garden, IL, USA.

Sedimentary samples for pollen analysis were collected from each of the stratigraphic levels (A-F) alongside the macrofossils. Sedimentary rock samples were processed and fossil pollen grains extracted according to the method explained in Grímsson et al. [30]. The fossil pollen grains were investigated both by light microscopy (LM) and scanning electron microscopy (SEM) using the single grain method as described by Zetter [31] and Halbritter et al. [32; pp. 121–123]. Ten fossil pollen grains were measured and studied with LM and SEM. For practical reasons, the fossil pollen is classified as a morphotype (MT) named after the locality where the grains were found. The fossil pollen from Mush is described in detail based on LM and SEM observations and compared to pollen from related extant taxa. Part of the original sediment and remaining organic residues from palynological preparations and the SEM stubs bearing the fossil pollen are curated in the Division of Structural and Functional Botany at the University of Vienna, Austria.

Pollen from extant flower material (S3 File) from the Royal Botanic Gardens, Kew (K) was prepared according to the protocol outlined in Grímsson et al. [33, 34] and Halbritter et al. [32; pp. 103–105, Acetolysis the Fast Way]. Twenty-five pollen grains from each sample were measured and studied with LM and SEM. The pollen terminology follows Punt et al. [35; LM] and Halbritter et al. [32; SEM].

Nomenclature

The electronic version of this article in Portable Document Format (PDF) in a work with an ISSN or ISBN will represent a published work according to the International Code of Nomenclature for algae, fungi, and plants, and hence the new names contained in the electronic publication of a PLOS ONE article are effectively published under the Code from the electronic edition alone, so there is no longer any need to provide printed copies.

The online version of this work is archived and available from the following digital repositories: PubMed Central and LOCKSS.

Results

  • Leguminosae Jussieu 1789

  • Detarioideae Burmeist. 1837

  • Amherstieae Benth. 1840

  • Englerodendron Harms 1907

  • Englerodendron mulugetanum Pan, Jacobs, Bush, Estrella, Grímsson, Herendeen, Burgt et Currano, sp. nov.

Holotype: MU17-43 (Fig 1A). National Museum of Ethiopia, Addis Ababa

Fig 1. Fossil and extant Englerodendron lamina.

Fig 1

A. Englerodendron mulugetanum sp. nov. paripinnate compound leaf (the twin leaflet is missing) with pulvinate petiolule. HOLOTYPE–MU17-43. B. Terminal leaflet of paripinnate leaf of Englerodendron korupense the twin leaflet is missing). ISOTYPE–MNHN-P-P00634905. Scale bar– 10 mm. Note twisted pulvinate petiolule. C. Leaflet of Englerodendron mulugetanum sp. nov. with detail of twisted pulvinate petiolule. MU27-18 #1. Scale bar– 10 mm.

Paratypes: MU23-40(1C) #4 (Cuticle; Fig 3A), MU27-18#1 (Fig 1C), MU29-40B #1, MU41-15 (Cuticle; Fig 3B)

Fig 3.

Fig 3

Fossil and extant Englerodendron lamina cuticle. Scale bars– 20 μm. A. Englerodendron mulugetanum sp. nov. abaxial leaflet surface. MU23-40(1C) #4. B. Englerodendron mulugetanum sp. nov. adaxial leaflet surface. MU41-15. C. Englerodendron concyliophorum abaxial leaflet surface. BM000081672. D. Englerodendron concyliophorum adaxial leaflet surface. BM000081672. E. Englerodendron explicans abaxial leaflet surface. MO2296034. F. Englerodendron explicans adaxial leaflet surface. MO2296034. G. Englerodendron usambarensis abaxial leaflet surface. K H/1194/96/56. H. Englerodendron usambarensis adaxial leaflet surface. K H/1194/96/56.

Additional Material: MU7-6#3, MU7-10, MU7-21#1, MU7-35-A5A#23, MU7-40#5, MU13-1, MU13-28#1, MU13-28#3, MU17-26A, MU18-16A#1, MU23-20, MU23-37#1 (Cuticle), MU23-59#1, and MU32-22#8, MU33-19, MU40-22 (S4 File).

Diagnosis: Paripinnate leaves, symmetrical leaflets, oppositely inserted with twisted and terete pulvinate short petiolules and acuminate leaflet tips. Secondary venation is eucamptodromous, often becoming brochidodromous towards the leaflet apex. Abaxial and adaxial cuticle with highly sinuous anticlinal cell walls, which also possess ‘knob-like’ thickenings. Stomata paracytic. Trichome bases present, but sparse.

Description: Modified and updated from Bush et al. [22]. Paripinnate leaves, possessing oppositely inserted symmetrical unlobed, untoothed (entire-margined), elliptic to slightly falcate leaflets with twisted and likely terete pulvinate short petiolules (Figs 1 and 2). Leaflet lamina generally range in size from circa 4.5 to 15.0 cm in length and 1.6 to 5.7 cm in width, typically with length: width ratios of 3:1 to 5:2. Leaflet midribs are canaliculate (Fig 2C). The leaflet apex is acute and possesses an acuminate ‘drip’ tip. The leaflet base is straight to rounded in shape and ranges from symmetrical to slightly asymmetrical [22; Fig 2A and 2C]. Primary venation is pinnate (Figs 1 and 2). Secondary venation is eucamptodromous, often becoming brochidodromous distally [22; Figs 1 and 2]. The secondary veins are irregularly spaced, have excurrent attachment, and generally possess uniform acute angles (Fig 2A and 2C). Leaflets typically possess (5 –) 6–7 (9–10) pairs of secondary veins. Inter-secondary veins are present, diverge from the midvein parallel to the secondary veins, are less than 50% of the length of the subjacent secondary, and have a frequency of < 1 per intercostal area (Fig 2). Tertiary venation is sinuous and generally opposite percurrent, rarely alternate percurrent (Fig 2). Fourth order veins are irregular reticulate, and fifth order veins freely ramify [22]. CUTICLE: Stomatal complexes are paracytic (incorrectly identified as pericytic in Bush et al., [22]) with one subsidiary cell larger than the other (Fig 3A). Stomata are prominent on the abaxial surface and are rare on the adaxial surface (Fig 3B). Guard cells range in size from 7.5 to 10.5 μm in length [23; Fig 2A]. The anticlinal cell walls on both the abaxial and adaxial leaf surfaces are highly sinuous [22], typically with greater than 9 ‘folds’ and often numbering ≥11 (Fig 3A and 3B). The abaxial epidermal cells are rectangular in shape and are 21.3 to 32.7 μm in length and 9.8 to 14.1 μm in width [22; Fig 3A]. Papillae are absent from both abaxial and adaxial leaf epidermal periclinal cell surfaces, but knob-like thickenings appear to be present on the anticlinal walls (Fig 3A and 3B; [36]). Hairs (trichomes) are present on the abaxial surface, but sparse, based on presence of thickened trichome bases. Trichomes are commonly associated with the veins. Hair bases present in intercostal areas are surrounded by radial basal cells. Hair bases associated with veins are surrounded by vein epidermal cells oriented similarly to adjacent vein cells.

Fig 2. Fossil and extant Englerodendron lamina continued.

Fig 2

A. Englerodendron mulugetanum sp. nov leaflet with a terete, pulvinate petiolule and secondary venation detail. MU29-40B #1. B. Leaflet of Englerodendron vignei. MNHN-P-P01037798. Scale bar– 10 mm. C. Englerodendron mulugetanum sp. nov. leaflet with detail of secondary, tertiary, and quaternary venation. MU29-41 #4. D. Leaflet of Englerodendron korupense. ISOTYPE–MNHN-P-P00634905. Scale bar– 10 mm.

Etymology: The species name honors our friend and colleague, Dr. Mulugeta Feseha, of Addis Ababa University, who introduced us to the fossil locality. In addition, ‘mulugeta’ (ሙሉጌታ), which means ‘he who rules’ in Amharic, is particularly fitting since this species was an ecological and temporal dominant in the early Miocene Mush forest paleoenvironment.

Comments: Based on a suite of macro-morphological leaf characteristics, the fossil morphotype originally designated as “Legume 1” [22, 23] can be identified taxonomically as a member of the Berlinia Clade of the tribe Amherstieae (Leguminosae: Detarioideae), and specifically matches a number of genera in the Berlinia Clade: Subclade B, namely Anthonotha, Berlinia, Englerodendron, and Isoberlinia [37] (S5 and S6 Files). These characteristics include paripinnate compound leaves, oppositely inserted, symmetrical leaflets that are elliptic to slightly falcate in shape, the presence of a short twisted pulvinate petiolule, a symmetrical to slightly asymmetrical base, secondary venation being eucamptodromous becoming brochidodromous towards the apex, and an acuminate leaflet apex forming a drip tip [22, 38, 39] (Fig 1 and S5 and S6 Files) The fossil morphotype differs from Oddoniodendron, another member of Berlinia Clade Subclade B, in lacking a long petiolule and in not possessing alternately inserted leaflets [37, 40]. The African endemic moist forest genus Gilbertiodendron is similar to the fossil taxon and possesses many of the characteristics mentioned above, but differs from the Mush taxon in possessing leaflets with brochidodromous to festooned brochidodromous secondary venation and the presence of leaf marginal and/or submarginal glands [38, 39, 41, 42]. Other members in the Berlinia Clade, particularly genera in the ‘bambjit’ clade (Brachystegia, Aphanocalyx, Michelsonia, Bikinia, Icuria, Tetraberlinia) and Microberlinia possess asymmetrical leaflets [37, 38, 43] (S5 and S6 Files), have a major basal vein or ‘fan’ of veins, and often have retuse or emarginate leaflet apices, all of which are absent from the fossil taxon. These characteristics commonly occur in a number of other Amherstieae taxa as well, and so taxa such as Cynometra clade A, Cynometra clade B, Hymenostegia, Plagiosiphon, Scorodophloeus, and Talbotiella can be eliminated as potential candidates for the fossil taxon [38, 4446] (S5 and S6 Files). The presence of twisted pulvinate petiolules is a relatively rare character and can only be found in a handful of Amherstieae genera including Crudia, Berlinia, Englerodendron, Gilbertiodendron, Librevillea, Oddoniodendron, Paramacrolobium, and Isoberlinia. The fossil morphotype differs from Crudia leaflet symmetry, secondary venation (Crudia possesses brochidodromous/festooned brochidodrmous venation), and leaves (alternately inserted leaflets in Crudia); Librevillea, in possessing alternately inserted, asymmetrical leaflets and imparipinnate leaves; Paramacrolobium in leaflet symmetry and lacking a major basal vein; and Gilbertiodendron and Oddoniodendron in the characteristics noted above [38] (S5 and S6 Files). It should be noted that Gilbertiodendron, Berlinia, Englerodendron, and Isoberlinia can possess both twisted and terete petiolules on the same plant or even compound leaf [38], S5 and S6 Files), unlike Crudia, where the character is constant. Anthonotha, Berlinia, Englerodendron, and Isoberlinia are the four genera having macro-morphological characteristics most similar to the fossil taxon, and among these, Berlinia and Englerodendron are the most closely comparable. Isoberlinia differs in typically possessing leaflets with noticeably asymmetrical leaflet bases and while leaflet apices may be acuminate (typically acute or rounded in savannah taxa), ‘drip tips’ are not present or not elongate.

The leaf epidermal cuticle characteristics allow the fossil to be placed in the genus Englerodendron as opposed to Anthonotha, Berlinia, and Isoberlinia. Englerodendron, and the more distantly related Gilbertiodendron, have highly sinuous anticlinal cell walls on both abaxial and adaxial leaf epidermal surfaces among species observed (Fig 2 and S7 File). The undulations on the anticlinal cell walls in species of these two genera are typically ‘Ω’ in shape (Fig 2 and S7 File). Berlinia possess sinuous anticlinal cell walls, but the undulations and fold amplitude are not as significant as in the fossil taxon, Englerodendron, or Gilbertiodendron and undulations are generally ‘∩’ in shape [47] (S7 File). Isoberlinia anticlinal cell walls are also undulate, but not usually sinuous (although, Isoberlinia scheffleri can possess sinuous anticlinal cell walls; S7 File). Anthonotha differs from the fossil in being characteristically hairy on the abaxial leaf surface and in possessing papillae on abaxial periclinal cell surfaces (S7 File).

Mush Morphotype (MT) pollen, affinity close to Englerodendron conchyliophorum and E. korupense

Description: Pollen, monad, prolate, P/E ratio 1.3–1.8, shape lobate-ellipsoid, elliptic in equatorial view, trilobate in polar view; equatorial diameter 17–42 μm in LM, 20–36 μm in SEM, polar axis 30–53 μm in LM, 35–61 μm in SEM; tricolporate; colpi long, extending between poles; pori inconspicuous, elongate elliptic(LM); exine 0.8–1.8 μm thick, nexine thinner than sexine (LM); tectate, colmellate (SEM); sculpture striate in LM, striate, perforate in SEM; aperture membrane granulate, nano- to microgemmate/areolate/rugulate, rugulate (SEM) (Fig 4 and Table 2).

Fig 4.

Fig 4

Light microscopy (A–F) and scanning electron microscopy (G–O) micrographs of the fossil Mush Englerodendron MT pollen, from Mush Valley, Ethiopia, Africa. A-E. Equatorial views, compressed pollen grains. F–G. Polar view, same compressed grain in LM and SEM. H–K. Equatorial views, compressed prolate pollen grains. L. Close-up of interapertural area, showing striate sculpture. M. Close-up of (J), showing interapertural area with striate and perforate sculpture. N. Close-up of (G), showing aperture with granulate and nano- to microgemmate/areolate sculpture membrane. O. Close-up of aperture, showing nanorugulate to regulate sculpture membrane. Scale bars– 10 μm (A–K), 1 μm (L–O).

Table 2. Pollen morphology of fossil and extant Berlinia Clade pollen investigated for this study.

Mush MT (fossil pollen) Englerodendron conchyliophorum Englerodendron explicans Englerodendron korupense Englerodendron leptorrhachis Englerodendron mengei Englerodendron usambarense Berlinia orientalis Isoberlinia scheffleri Oddoniodendron micranthum
Equatorial diameter (LM) 17–42 40–48 35–38 40–46 38–42 34–36 35–42 44–48 38–42 30–32
Equatorial diameter (SEM) 20–36 28–43 32–35 34–44 34–41 31–38 21–37 35–46 28–39 27–32
Polar axis (LM) 30–53 48–52 36–41 52–56 34–38 36–40 36–38 44–46 42–44 29–31
Polar axis (SEM) 35–61 47–62 41–47 51–60 33–39 34–45 36–46 39–51 42–49 26–30
P/E ratio measured (LM) 1.3–1.8 1–1.3 1–1.1 1.1–1.4 0.8–1 1–1.1 0.9–1.1 0.9–1 1–1.1 0.9–1
P/E ratio category (LM) Prolate Isodiametric to prolate Isodiametric to prolate Prolate Oblate to Isodiametric Isodiametric to prolate Oblate to prolate Oblate to Isodiametric Isodiametric to prolate Oblate to isodiametric
Outline in equatorial view (LM) Elliptic Circular to elliptic Circular to elliptic Elliptic Circular to elliptic Circular to elliptic Circular to elliptic Circular Circular to elliptic Circular to elliptic
Outline in polar view (LM) Trilobate Trilobate Trilobate Trilobate Circular (to trilobate) Trilobate Circular (to trilobate) Circular to trilobate Trilobate Hexagonal
Pollen shape Lobate-ellipsoid Lobate-spheroid to ellipsoid Lobate-spheroid to ellipsoid Lobate-ellipsoid Ellipsoid to spheroid Lobate-spheroid to ellipsoid (Lobate-)ellipsoid to spheroid (Lobate-)ellipsoid to spheroid Lobate-spheroid to ellipsoid Hexagonal-dipyramid
Exine thickness (LM) 0.8–1.8 1.6–2.6 1.8–2.4 1.6–2.4 1.2–1.6 1.8–2.4 1–2 2–3 1.6–2.4 1–1.6
Sculpture LM Striate Striate Striate Striate Striate Striate Striate Striate Striate Rugulate
Sculpture SEM Striate, perforate Striate, perforate Striate Striate, perforate Striate Striate Striate, perforate Striate Striate Rugulate, verrucate, fossulate, perforate
Striae width (SEM) 0.8–1.5 0.5–1.7 1.2–1.6 1.2–2 0.4–1.1 1.2–2 0.8–1.3 1.2–1.8 0.8–1.5 N/A
Apertures Tricolporate Tricolporate Tricolporate Tricolporate Tricolporate Tricolporate Tricolporate Tricolporate Tricolporate Tricolporate
Visability pori (LM) Inconspicuous Inconspicuous Inconspicuous Conspicuous to inconspicuous Conspicuous Conspicuous Conspicuous Conspicuous Conspicuous Conspicuous
Outline pori (LM) Lolongate elliptic Lolongate elliptic Lolongate elliptic Lolongate elliptic Lolongate elliptic Lolongate elliptic Circular to lolongate elliptic Lolongate elliptic Lolongate elliptic Lalongate elliptic
Aperture membrane (SEM) Granulate, nano- to microgemmate / areolate / rugulate, rugulate Granulate, nano- to microrugulate Nanorugulate to rugulate Granulate, nanorugulate to rugulate Granulate, nano- to microareolate / rugulate Granulate, nano- to microrugulate Granulate, nano- to microgemmate / areolate / rugulate Nanorugulate to rugulate, granulate to areolate Nano- to microrugulate, rugulate Granulate, nano- to microgemmate / areolate
Overlapping features (LM & SEM) N/A 17 16 17 12 14 13 11 15 6

Note: All measurements include only those from this study and are given in μm. Features of extant pollen that overlap with the fossil Mush MT appear in bold font. N/A = not applicable.

Comparison: The Mush MT pollen shows a considerable size range when considering the equatorial diameter and length of the polar axis, also many of the grains are small. None of the pollen from the extant taxa shows such a wide size range nor are as small as the fossil pollen, but the Mush MT overlaps with most of them, and all size ranges measured for Englerodendron explicans pollen fall within the fossil MT. The Mush MT is clearly prolate, with a P/E ratio between 1.3–1.8, but pollen from most of the extant taxa are close to isodiametric, except for pollen of E. conchyliophorum and E. korupense, which are also prolate (Figs 35 and Table 2). The Mush MT is trilete in polar view and lobate-ellipsoid in shape like pollen from most of the extant taxa, except pollen of Oddoniodendron micranthum, which is hexagonal in polar view and hexagonal-dipyramid in shape (Fig 4 and Table 2). The exine thickness of the Mush MT pollen displays a wide range, consistent with the size range of the morphotype (Table 2). The exine thickness overlaps with measurements from all the extant taxa, except Berlinia orientalis, which has a considerably thicker exine (Table 2). The exine thickness of Englerodendron leptorrhachis falls completely within the Mush MT, and the exine thickness of E. usambarense is also very close to that of the fossil MT. All pollen from extant Englerodendron, Berlinia, and Isoberlina, are striate when observed with LM, in the same way as the fossil MT, but pollen of Oddoniodendron micranthum is rugulate and clearly different when observed with either LM or SEM (Table 2). Only Englerodendron conchyliophorum, E. korupense, and E. usambarense show the perforate sculpture between the striae observed with SEM that is typical for the Mush MT. The width of the striae in the Mush MT overlaps with that of all investigated extant taxa except Oddoniodendron, which has a rugulate and verrucate sculpture when observed with SEM. The width of the striae in Englerodendron conchyliophorum and E. usambarense is close to that of the Mush MT, but the width of striae in Isoberlinia scheffleri is identical to that of the fossil. Both the Mush MT and pollen from all the investigated extant taxa is tricolporate, but the fossil pollen grains have inconspicuous pori that are hardly observed in either LM or SEM (Figs 46 and Table 2). This feature was also noticed for Englerodendron conchyliophorum, E. explicans, and E. korupense (Figs 4 and 5 and Table 2). The pori are lolongate elliptic in outline in the Mush MT and in pollen from most of the extant taxa, except Oddoniodendron micranthum, where the pollen is lalongate elliptic. The sculpture of the aperture membrane in the Mush MT is quite variable and overlaps with that observed in pollen from all the extant taxa. The combined features within each taxon shows that the Mush MT shares most morphological features with pollen of Englerodendron conchyliophorum (17 traits), E. korupense (17 traits), and E. explicans (16 traits), followed by Isoberlinia scheffleri (15 traits; Table 2).

Fig 5.

Fig 5

Light microscopy (A, B, E, F, I, J, M, N) and scanning electron microscopy (C, D, G, H, K, L, O, P) micrographs of extant Berlinia Clade pollen from Africa. A–D. Berlinia orientalis (from Tanzania, coll. FC Magogo & R Rose Innes, 409 [K000023099]). A. Polar views, high focus (left), optical cross-section (right). B. Equatorial views, high focus (left), optical cross-section (right). C. Equatorial view. D. Close-up showing aperture membrane and adjacent striate sculpture. E–H. Englerodendron conchyliophorum (from Cameroon, coll. s.n., s.n. [K000557101]). E. Polar views, high focus (left), optical cross-section (right). F. Equatorial views, high focus (left), optical cross-section (right). G. Equatorial view. H. Close-up showing aperture membrane and adjacent striate and perforate sculpture. I–L. Englerodendron explicans (from Guinea, coll. Haba, 1257 [K001381154]). I. Equatorial views, high focus (left), optical cross-section (right). J. Equatorial views, high focus (left), optical cross-section (right). K. Equatorial view. L. Close-up showing aperture membrane and adjacent striate sculpture. M–P. Englerodendron korupense (from Cameroon, coll. XM van der Burgt [K000264712]). M. Polar views, high focus (left), optical cross-section (right). N. Equatorial views, high focus (left), optical cross-section (right). O. Equatorial view. P. Close-up showing aperture membrane and adjacent striate sculpture. Scale bars– 10 μm (A–C, E–G, I–K, M–O), 2 μm (D, H, L, P).

Fig 6.

Fig 6

Light microscopy (A, B, E, F, I, J, M, N) and scanning electron microscopy (C, D, G, H, K, L, O, P) micrographs of extant Berlinia Clade pollen from Africa continued. A–D. Englerodendron leptorrhachis (from Cameroon, coll. Satabié, 980 [K001341298]). A. Polar views, high focus (left), optical cross-section (right). B. Equatorial views, high focus (left), optical cross-section (right). C. Equatorial view. D. Close-up showing aperture membrane and adjacent striate sculpture. E–H. Englerodendron mengei (from DR Congo, coll. J Louis, 3666 [K000557102]). E. Polar views, high focus (left), optical cross-section (right). F. Equatorial views, high focus (left), optical cross-section (right). G. Equatorial view. H. Close-up showing aperture membrane and adjacent striate sculpture. I–L. Englerodendron usambarense (from Tanzania, coll. Greenway, 1061 [K000555978]). I. Equatorial views, high focus (left), optical cross-section (right). J. Equatorial views, high focus (left), optical cross-section (right). K. Equatorial view. L. Close-up showing aperture membrane and adjacent striate sculpture. M–P. Isoberlinia scheffleri (from Tanzania, coll. Greenway, 3319 [K000557103]). M. Polar views, high focus (left), optical cross-section (right). N. Equatorial views, high focus (left), optical cross-section (right). O. Equatorial view. P. Close-up showing aperture membrane and adjacent striate sculpture. Scale bars– 10 μm (A–C, E–G, I–K, M–O), 2 μm (D, H, L, P).

Comments: The morphology (LM and SEM) of the fossil Mush MT pollen is similar to those of extant pollen produced by Englerodendron, Isoberlinia, and Berlinia (compared in Table 2). The Mush MT has a much broader size and P/E range and shows more variability in the general sculpture and in the sculpture of the aperture membrane than pollen from extant taxa. The reason for this is uncertain, but might be explained by one of the following: 1) the fossil pollen grains originate from the same biological taxon but reflect a much greater sampling source and originate from different anthers/flowers/individuals as compared to a single anther providing the extant comparison material. 2) the fossil pollen grains originate from more than a single biological taxon but their pollen overlap in morphological features and cannot be distinguished. 3) The fossil pollen grains originate from a single biological taxon and their morphological plasticity reflects an ancestral trait partly preserved in different extant descendants. Whatever the reason, it is clear that the Mush MT is most comparable to pollen from some extant Englerodendron and therefore supports a likely affiliation with the Englerodendron mulugetanum sp. nov. fossil leaves.

Discussion

Taxonomic, evolutionary, and biogeographic implications

Englerodendron is a moderately sized genus in the Amherstieae (Leguminosae: Detarioideae) consisting of 18 extant species belonging within a monophyletic subclade within the Berlinia Clade, referred to as Berlinia Clade Subclade B, which consists of Anthonotha, Berlinia, Englerodendron, Isoberlinia, Librevillea, and Oddoniodendron [4852]. Englerodendron was formerly considered monospecific, consisting of a submontane forest species E. usambarense, endemic to the West Usambara Mountains in the Eastern Arc Mountains of Tanzania [53, 54]. The genus, which is sister to Anthonotha, now includes a number of species formerly included in the latter genus, as well as species of the now synonymized Isomacrolobium and Pseudomacrolobium [48, 50].

Englerodendron sensu lato can now be characterized ecologically more broadly as a moist and wet forest genus (although E. explicans can also occur in savanna woodlands) that is mainly restricted to the Guineo-Congolian region along with the isolated Eastern Arc Englerodendron usambarense [53, 54] (Fig 7). Species can occur in a variety of forest types including primary rain forest, semi-deciduous moist forests, riverine forest, gallery forest, submontane forest, and even lagoon-margin forest habitat [10, 48, 49, 52]. While extant species of Englerodendron do not develop into monodominant forest formations today, morphological and ecological characteristics hypothesized to assist in the development of such formations are prevalent within the genus and subclade. These characteristics include large seed size and short dispersal capabilities, shade-tolerant seedlings, ectomycorrhizal associations, conspecific gregariousness, and observations of coppicing within the genus are noted [2, 49, 55, 56].

Fig 7. Distribution map and terrestrial ecoregion occurrence of extant Englerodendron (circles) and location of the fossil species, Englerodendron mulugetanum (star).

Fig 7

This map was created with Simplemappr (https://www.simplemappr.net/).

The early Miocene Englerodendron mulugetanum sp. nov. is the only known fossil occurrence of the genus, although pollen attributed to closely related genera (Anthonotha, Berlinia, and Isoberlinia) is known from the late Paleocene and early Eocene of Nigeria and the late Oligocene—early Miocene of northern Kenya–indicating a long evolutionary history of the Berlinia Clade: Subclade B in Africa [37, 5759]. Some fossil lamina impressions from the early Miocene Bugishu Series in Uganda also appear to be similar to Berlinia, but definitively assigning a generic identification to this material is not possible. These fossil records and the early Miocene (21.73 Ma) occurrence of Englerodendron mulugetanum sp. nov. indicate that late Pliocene or early Pleistocene evolutionary divergence time estimates for the genus and its sister taxon, Anthonotha, by Estrella et al. [37] need to be re-assessed.

In the Afrotropics, the majority of moist and wet monodominant forests consist of detarioid legume species as their principal constituent [4, 6, 6064] (Table 1). Temporary monodominant forest formations dominated by non-legume taxa can develop in pioneer seral stage vegetation (e.g., Musanga spp.—Urticaceae; [3, 5, 65, 66]. Within the moist and wet detarioid legume African monodominant forest formations, all ecologically dominant species that fulfill this role belong within the Amherstieae, the largest and most diverse tribe in the Detarioideae composed of about 50 genera and about 570 species [44, 67]. Nevertheless, Subclade B of the Berlinia Clade of the tribe is absent among modern forest species dominants [37]. The majority of species that currently constitute monodominant forests in Africa are found in Subclade A of the Berlinia Clade, which is composed of the ‘bambijt’ clade + (Gilbertiodendron + Didelotia) [37]. The sole other species is found in the mid-level position in the phylogeny of the Amherstieae (Cynometra alexandri) [37]. Many genera within the Berlinia Clade of Amherstieae possess characteristics (as noted above) that could provide an ecological pathway to becoming an ecological dominant in moist and wet Afrotropical forests given an opportunity. Within the other speciose tribe within the Detarioideae, the Detarieae, multiple genera and species can be found in tropical African forest formations, but only one taxon, Gilletiodendron glandulosum, is known to dominate a forest community [68]. In this case, the community represents a relictual Sudanian-type of dry forest and falls outside the purview of this study [68]. Three additional Detarieae genera, Colophospermum, Copaifera, and Guibourtia, develop monotypic stands in African communities [10].

Paleoecology and evidence for a monodominant forest

Extensive analyses of plant macro- and microfossils, and isotope and organic geochemistry from the Mush Valley lacustrine deposits provided a view of the surrounding community and the lake itself, which accumulated fine sediments and organic matter over some 50–60 ka [22, 23]. The following results of those studies together indicated the ancient terrestrial community was a forest:

  1. The average leaf carbon isotope discrimination relative to atmospheric CO213C) derived from organically preserved leaf compressions is 23.4 ‰, equal to that of modern tropical rainforests [22, 69].

  2. The reconstructed mean annual precipitation among Levels A—F, ranges from 1523+199125 to 1638 +215125 mm/yr, comparable to values supportive of forest vegetation [22].

  3. Productive phytolith samples collected from 2–7 m above and below the macrofossil deposits are dominated by non-grass forest forms [23].

  4. The δ13C values of terrestrially sourced C29 and C31 n-alkanes (angiosperm dicots) from bulk organic samples among Levels A-F are −35 to −32‰, indicative of purely C3 vegetation [23].

  5. Terrestrial plant macrofossil identifications to this point include species limited to forest communities today: Newtonia mushensis [24], Tacca umerii [2225, 27], and now Englerodendron mulugetanum sp. nov.

  6. Terrestrial fossil pollen analyzed using combined LM and SEM, and even TEM, for single-grains also include taxa occurring in Africa’s forests: Aristogeitonia / Mischodon / Oldfieldia / Voatamalo clade [70; fig. 19], Sclerosperma [71; fig. 3], and Hagenia [72; figs 6–8].

Although Currano et al. [23, 27] concluded the Mush forest was a mixed-moist, semi-evergreen closed-canopy forest similar to those found today in West, Central, and eastern Africa [e.g., 73], the long-term abundance and consistent dominance of Englerodendron mulugetanum sp. nov. leaflets at all lake levels sampled, and its placement in the Berlinia Clade, tribe Amherstieae, among which are species most commonly forming monodominant wet forests today, prompted our reconsideration of Mush forest structure. The consistent and overwhelming abundance of E. mulugetanum leaflets among the fossil assemblages is a compelling aspect of the collections, and led to the hypothesis of a monodominant forest at Mush by Bush et al. [22]. This taxon comprises 53% of all classified leaves (1289 of 2427; leaflets are counted as leaves) and as much as 66% of specimens among the six stratigraphic levels ([23], and Table 3). Taphonomic processes, documented by studies of modern leaf fall, transport, litter accumulation, and preservation indicate that canopy leaves are more common than those from the understory in forest litter and local sedimentary deposits, and that leaves travel short distances before deposition, especially if thick and heavy; compound-leaved and deciduous trees can have an outsized impact on the composition of local (e.g., lakeside) deposits [7477]. Thus, to understand results of these processes as they influence leaf accumulations from monodominant vs. mixed forests, litter studies of comparable modern tropical wet forests must be consulted. Analyses of modern leaf litter in African forests are rare, but Peh et al. [78] compared the litterfall, its rate of decomposition, and representation of the dominant taxon in litter samples in single-dominant vs. mixed forest plots in Cameroon (Table 3). Monodominant forests of Gilbertiodendron dewevrei (a Berlinia Clade legume) produced leaf litter whose dry weight was 52% - 92% (average of 73% ± 23%) G. dewevrei leaves [78]. Peh et al. [78] did not measure the proportion of leaf litter belonging to the most abundant species present in each mixed forested sampled, but the proportion of leaves belonging to the most abundant taxon in modern litter censuses from diverse Neotropical forests ranges from 12.8 to 31.4% (Table 3).

Table 3. Comparison of diversity and dominance measures among fossil and modern localities [27, 63, 78].

Numbers shaded in blue highlight collections where the dominant taxon comprises ≥ 50%. Numbers shaded in green highlight leaf collections with Hill values ≥ 4.0.

Locality Age Data Type Number of Leaves Species Richness at 300 Leaves Hill # q = 2 Percent Dominant Taxon
Guang 27.1 Ma Fossil leaves 433 34.8 4.57 43.7
Bull’s Bellow 27.1 Ma Fossil leaves 606 27.9 6.38 33.8
Mush A 21.7 Ma Fossil leaves 349 25 6.76 30.9
Mush B 21.7 Ma Fossil leaves 400 28.8 3.07 55.8
Mush C 21.7 Ma Fossil leaves 95 NA 3.97 49.5
Mush D 21.7 Ma Fossil leaves 532 30.9 3.50 50.9
Mush E 21.7 Ma Fossil leaves 510 27.0 3.12 55.7
Mush F 21.7 Ma Fossil leaves 541 20.4 2.16 65.8
BCI Modern Leaf litter 672 56.4 15.9 18.0
Yasuni Modern Leaf litter 951 50.7 7.9 31.4
Rio Negro Modern Leaf litter 932 70.1 22.1 12.8
Peh mono1 Modern Leaf litter 52
Peh mono2 Modern Leaf litter 73
Peh mono3 Modern Leaf litter 92
Kearsley monodominant Modern Tree plots, dbh data 8.4 ± 1.2 65.3
Kearsley mixed Modern Tree plots, dbh data 21.2 ± 3.6 16.7

Measures of diversity are also lower for monodominant forests than mixed forests because of the presence of several species in low numbers (Table 3) [18, 63, 78]. In assessing diversity among the Mush leaf assemblages we chose to examine both rarefied species richness and Shannon diversity (Hill number, q = 2), which are commonly used in neoecological studies because values are more readily comparable among different communities [79]. A Hill number is the “effective number of species,” which is defined as the number of equally abundant species needed to produce the given value of a diversity index [23, 79]. Rarefied richness gives equal weight to rare and common taxa, whereas Shannon diversity emphasizes abundant taxa and can be thought of as the number of equally abundant common species. Table 3 provides diversity comparisons among Mush assemblages, modern leaf assemblages, and Kearsley et al.’s [63] study from monodominant and mixed forests in the Democratic Republic of Congo.

Fossil leaf collections from an Oligocene Ethiopian site (Chilga) to the north of Mush, and that have diversity measures demonstrating a richer and more even frequency distribution of taxa, provide a fossil point of comparison. The two Chilga localities listed in Table 3, Guang and Bull’s Bellow, are contemporaneous, but located about 1.5 km apart. They share no taxa, and represent diverse, mixed forests at different stages of succession [80]. The most dominant taxon among leaves collected at each site comprises 44% and 34% of 433 and 606 leaves, respectively [27]. The Hill numbers are in line with, albeit lower than, leaf litter collections from a very diverse modern mixed forest at Yasuni, Ecuador [27].

As noted, Englerodendron mulugetanum sp. nov. is the most abundant taxon at each stratigraphic level collected at Mush. Level A, near the base of the section, contains only 31% E. mulugetanum sp. nov. leaflets and has a higher Shannon diversity than either Chilga site (Table 3 and Fig 8). Thus, we interpret the leaf assemblage from Level A as having come from a mixed rather than monodominant forest. Significant volcanic activity is associated with the formation of the paleolake, and it is possible that the forest at the time of Level A was on its way to monodominance. By the time of Level B, Shannon diversity drops significantly and E. mulugetanum sp. nov. leaflets comprise 55.8% of the assemblage [23], within the range that Peh et al. [78] observed in G. dewevrei monodominant forests (Fig 8). Shannon diversity remains low, and the proportion of E. mulugetanum sp. nov. leaflets high, for the remainder of the Mush stratigraphic levels (Fig 8). Perhaps the most compelling aspect of the Mush assemblages in support of monodominance is the consistent abundance of E. mulugetanum sp. nov. over the 50–60 kyrs sampled [23]. This fact argues against the presence of a single tree overarching or close to the shore of the ancient lake. In addition, although compound-leaved legume taxa are generally the most abundant overall, only E. mulugetanum sp. nov. dominates the assemblages at each stratigraphic level.

Fig 8. Bar plot of Englerodendron mulugetanum sp. nov. abundance through the stratigraphic section.

Fig 8

The presence of a long-lived, prehistoric monodominant forest in northwestern Ethiopia raises questions about the role of such forests in the evolutionary history and the paleoecological processes of African forest vegetation during the early Miocene. Currently, no other Cenozoic tropical monodominant forests have been identified from before the Holocene. However, the likelihood that this assemblage represents the sole monodominant forest existing on the continent during the early Miocene is also relatively remote. As noted above, a number of monodominant forest types, differing in the dominant species constituent and type (persistence, seral stage, edaphically maintained, etc.), occur on the continent today and the only shared characteristic among them is that a single arborescent species makes up more than 50% of the canopy constituents of such forests [3, 81, 82]. Thus, monodominant forests do not harbor the magnitude of plant biodiversity and structural complexity as moist and wet mixed tropical forest formations, and consequently have bottom-up food web impacts for example, the diversity and intensity of frugivory and herbivory, as well as vertebrate biodiversity and biomass [8386]. In most modern studies, observations of primate abundances and species-richness, elephant densities and activities, and rodent species-richness are reduced in Gilbertiodendron dewevrei-dominated monodominant forest formations in comparison to adjacent mixed and secondary forest formations [84, 85, 87, 88]. Typically, mammals prefer secondary and mixed forests due to the abundance of food resources in such forest types in comparison to primary or late secondary monodominant forests [83, 84, 89]. Correspondingly, the reduction of faunal elements in some forested habitats may actually increase the likelihood of monodominant forests developing or expanding [90]. There is some evidence that reduced elephant activity in western Uganda may assist in the development of Cynometra alexandri monodominant forests [91].

The presence of monodominant forests also creates additional vegetation heterogeneity within the tropical African sphere and how this affected forest faunal distributions and evolution is not known, but provides an additional aspect to consider–particularly in understanding dynamic changes in tropical forest distribution during the Miocene and how forest extent and composition may have affected particular mammal groups such as primates. The origin, temporal record, and spatial scale of Cenozoic monodominant forests in Africa are unknown, as Mush remains but a single datum point; however, this gap may be filled potentially by additional investigations of well-sampled, well-preserved plant macrofossil assemblages.

Supporting information

S1 File. Inclusivity in global research information and checklist.

(DOCX)

S2 File. Herbarium specimens examined.

(XLSX)

S3 File. Herbarium specimens sampled for micro-morphological (leaf cuticle) and palynological analysis.

(XLSX)

S4 File. Additional Englerodendron mulugetanum sp. nov. specimens.

(PDF)

S5 File. Table of comparing African Amherstieae (Leguminosae, Detarioideae) leaf and leaflet characteristics.

(XLSX)

S6 File. African Amherstieae (Leguminosae, Detarioideae) leaf and leaflet images and characteristics.

(PDF)

S7 File. Abaxial and adaxial leaf cuticle images of Berlinia Clade (Leguminosae, Detarioideae, Amherstieae) taxa.

(PDF)

Acknowledgments

We thank the Authority for Research and Conservation of Cultural Heritage for permission to conduct research in the Mush Valley and the director and staff of the National Museum of Ethiopia for facilitating our research. We are grateful to the people of Upper and Lower Mush for their hospitality, and to N. Tabor, M. Clemens, M. Feseha, L. Jacobs, J. Noret, D. Danehy, and T. Tesfamichael for contributions to field work. In particular we are grateful to M. Feseha for his role in bringing the Mush Valley locality to our attention. We are also grateful to D. Erwin, UC Museum of Paleontology, for providing images of fossils from the Bugishu Series in Uganda and T. Rehman, Botanical Research Institute of Texas, for providing herbarium material for us to examine. We are also thankful to the two anonymous reviewers whose comments improved this work.

Data Availability

All relevant data are within the paper and its Supporting Information files.

Funding Statement

Funded by U.S. National Science Foundation (https://www.nsf.gov/) grants EAR 1053549 (BFJ) and EAR 1052478 (EDC), National Geographic Society Grant (https://www.nationalgeographic.org/society/grants-and-investments/) CRE 8816-10 (EDC), and the Austrian Science Fund (https://www.fwf.ac.at/en/), FWF, P29501-B25 (FG). The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.

References

  • 1.Gentry AH. Tree species richness of upper Amazonian forests. PNAS. 1988;86:156–159. doi: 10.1073/pnas.85.1.156 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 2.ter Steege H, Henkel TW, Helal N, Marimon BS, Marimon BH Jr, Huth A. et al. 2019. Rarity of monodominance in hyperdiverse Amazonian forests. Scientific Reports. 2019;9:13822. doi: 10.1038/s41598-019-50323-9 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 3.Connell JH, Lowman MD.Low-diversity tropical rain forests: some possible mechanisms for their existence. The American Naturalist. 1989;134:88–119. [Google Scholar]
  • 4.Torti SD, Coley PD, Kursar TA. Causes and consequences of monodominace in tropical lowland forests. The American Naturalist. 2001;157:141–153. [DOI] [PubMed] [Google Scholar]
  • 5.Richards PW. 1996. The tropical rain forest, 2nd edition. Cambridge (UK):Cambridge University Press; 1996. [Google Scholar]
  • 6.Hart TB, Hart JA, Murphy PG. Monodominant and species-rich forests of the humid tropics: causes for their co-occurrence. The American Naturalist. 1989;133:613–633. [Google Scholar]
  • 7.Nascimento MT, Proctor J. Soil and plant changes across a monodominant rain forest boundary on Maracá Island, Roraima, Brazil. Global Ecology and Biogeography Letters. 1997;1:387–395. [Google Scholar]
  • 8.Mackinder BA, Saslis-Lagoudakis H, Wieringa JJ, Devey D, Forest F, Bruneau A. The tropical African legume Scorodophloeus clade includes two undescribed Hymenostegia segregate genera and Micklethwaitia, a rare, monospecific genus from Mozambique. South African Journal of Botany 2013;89:156–163. [Google Scholar]
  • 9.Estrella M de la, Wieringa JJ, Mackinder B, van der Burgt X, Devesa JA, Brounot A. Phylogenetic analysis of the African genus Gilbertiodendron J. Léonard and related genera (Leguminosae-Caesalpinioideae-Detarieae). Intl J Plant Sci. 2014;175:975–985. [Google Scholar]
  • 10.Lebrun J-P, Stork AL. Tropical African flowering plants: ecology and distribution, Volume 3: Mimosaceae–Fabaceae (incl. Derris). Conservatoire et Jardin botaniques de la Ville de Genève, Oceanography 2008;16:349–356. [Google Scholar]
  • 11.Heckenhauer J, Samuel R, Ashton PS, Turner B, Barfuss MHJ, Jang T-S, et al. Phylogenetic analyses of plastid DNA suggest a different interpretation of morphological evolution than those used as the basis for previous classifications of Dipterocarpaceae (Malvales). Bot. J. Linn. Soc. 2017;185:1–26. [Google Scholar]
  • 12.Ashton PS, Morley RJ, Heckenhauer K, Prasad V. The magnificent dipterocarps: précis for an epitaph? Kew Bulletin 2021. 10.1007/s12225-021-09934-7. [DOI] [Google Scholar]
  • 13.Couvreur TLP, Dauby G, Blach-Overgaard A, Deblauwe V, Dessein S, Droissart V, et al. Tectonics, climate and diversification of the tropical African terrestrial flora and fauna. Biological Reviews. 2021;96:16–51. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 14.Makana J-R, Ewango CN, McMahon SM, Thomas SC, Hart TB, Condit R. Demography and biomass change in monodominant and mixed old-growth forest of the Congo. J Trop Ecol. 2011;27:447–461. [Google Scholar]
  • 15.Masens da-Musa YB, Ngbolua K, Masens M, Tambu TM, Gédéon NB. Phytoecological study of Nzundu massif forest of Imbongo city, Kwilu Province, Democratic Republic of the Congo. Trop Plant Res. 2017;4:363–375. [Google Scholar]
  • 16.Pfadenhauer JS, Klötzli F. Global vegetation: fundamentals, ecology and distribution. Berlin (Ger): Springer; 2020. [Google Scholar]
  • 17.Peh KS-H, Lewis SL, Lloyd J. Mechanisms of monodominance in diverse tropical tree-dominated systems. J Ecol. 2011;99:891–898. [Google Scholar]
  • 18.Djuikouo MNK, Peh KS-H, Nguembou CK, Doucet JL, Lewis SL, Bonaventure S. Stand structure and species co-occurrence in mixed and monodominant Central African tropical forests. J Trop Ecol. 2014; 30:447–455. 10.1017/S0266467414000352. [DOI] [Google Scholar]
  • 19.Gomes AL, Revermann R, Meller P, Gonçalves FMP, Aidar MPM, Lages F, et al. Functional traits and symbiotic associations of geoxyles and trees explain the dominance of detarioid legumes in miombo ecosystems. New Phytologist. 2021;230:510–520. doi: 10.1111/nph.17168 [DOI] [PubMed] [Google Scholar]
  • 20.Crawley M. Palaeocene wood from the Republic of Mali. Bulletin of the British Museum of Natural History (Geology). 1988;44: 3–14. [Google Scholar]
  • 21.Herrera F, Carvalho MR, Wing SL, Jaramillo C, Herendeen PS. Middle to late Paleocene leguminosae fruits and leaves from Colombia. Australian Systematic Botany. 2019;32:385–408. [Google Scholar]
  • 22.Bush RT, Wallace J, Currano ED, Jacobs BF, McInerney FA, Dunn RE, et al. Cell anatomy and leaf δ13C as proxies for shading and canopy structure in a Miocene forest from Ethiopia. Palaeogeography, Palaeoclimatology, Palaeoecology. 2017;485:593–604. [Google Scholar]
  • 23.Currano ED, Jacobs BF, Bush RT, Novello A, Feseha M, Grímsson, et al. Ecological dynamic equilibrium in an early Miocene (21.73 Ma) forest, Ethiopia. Palaeogeogrpahy, Palaeoclimatology, Palaeoecology. 2020; 10.1016/j.palaeo.2019.109425 [DOI] [Google Scholar]
  • 24.Pan AD, Currano ED, Jacobs BF, Feseha M, Tabor N, Herendeen PS. Fossil Newtonia (Fabaceae: Mimoseae) seeds from the early Miocene (22–21 Ma) Mush Valley in Ethiopia. International Journal of Plant Sciences. 2012;173:290–296. [Google Scholar]
  • 25.Pan AD, Jacobs BF, Currano ED. Dioscoreaceae fossils from the late Oligocene and early Miocene of Ethiopia. Bot J Lin Soc. 2014;175:17–28. [Google Scholar]
  • 26.Engel MS, Currano ED, Jacobs BF. The first mastotermitid termite from Africa (Isoptera: Mastotermitidae): a new species of Mastotermes from the early Miocene of Ethiopia. Journal of Paleontology. 2015;89:1038–1042. [Google Scholar]
  • 27.Currano ED, Jacobs BF, Pan AD. Is Africa really an “odd man out”? Evidence for diversity decline across the Oligocene-Miocene boundary. International Journal of Plant Sciences. 2021; 10.1086/714308. [DOI] [Google Scholar]
  • 28.Tesfamichael T, Jacobs BF, Tabor NJ, Michel L, Currano ED, Feseha M, et al. Settling the issue of “decoupling” between atmospheric carbon dioxide and global temperature: [CO2]atm reconstructions across the warming Paleogene-Neogene divide. Geology. 2017;45:999–1002. [Google Scholar]
  • 29.Herendeen PS, Dilcher DL. Fossil mimosoid legumes from the Eocene and Oligocene of southeastern North America. Review of Palaeobotany and Palynology. 1990;62:339–61. [Google Scholar]
  • 30.Grímsson F, Denk T, Zetter R. Pollen, fruits, and leaves of Tetracentron (Trochodendraceae) from the Cainozoic of Iceland and western North America and their palaeobiogeographic implications. Grana. 2008;47:1–14. 10.1080/00173130701873081 [DOI] [Google Scholar]
  • 31.Zetter R. Methodik und Bedeutung einer routinemäßig kombinierten lichtmikroskopischen und rasterelektonenmikroskopischen Untersuchung fossiler Mikrofloren. Courier Forschungsinstitut Senckenberg. 1989;109:41–50. [Google Scholar]
  • 32.Halbritter H, Ulrich S, Grímsson F, Weber M, Zetter R, Hesse M, et al. Illustrated pollen terminology, 2nd ed. Springer. 2018; 10.1007/978-3-319-71365-6 [DOI] [Google Scholar]
  • 33.Grímsson F, Grimm GW, Zetter R. Tiny pollen grains: First evidence of Saururaceae from the Late Cretaceous of western North America. PeerJ 5: e3434. doi: 10.7717/peerj.3434 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 34.Grímsson F, Grimm GW, Zetter R. 2018. Evolution of pollen morphology in Loranthaceae. Grana 2017;57:16–116. doi: 10.1080/00173134.2016.1261939 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 35.Punt W, Hoen PP, Blackmore S, Nilsson S, Le Thomas A. Glossary of pollen and spore terminology. Rev Pal Pal. 2007;143:1–81. 10.1016/j.revpalbo.2006.06.008 [DOI] [Google Scholar]
  • 36.Dilcher D.L. Approaches to identification of angiosperm leaf remains. Bot. Rev. 1974;40:1–157. [Google Scholar]
  • 37.Estrella M de la, Cervantes S, Janssens SB, Forest F, Hardy OJ, Ojeda DI. The impact of rainforest area reduction in the Guineo-Congolian region on the tempo of diversification and habitat shifts in the Berlinia clade (Leguminosae). J Biogeogr. 2020;47:2728–2740. [Google Scholar]
  • 38.Hawthorne W, Jongkind C. Woody plants of Western African Forests: a guide to the forest trees, shrubs, and lianes from Senegal to Ghana. Kew (London): Kew Publishing: Kew; 2006. [Google Scholar]
  • 39.Estrella M de la, Devesa JA, Wieringa JJ. A morphological re-evaluation of the taxonomic status of the genus Pellegriniodendron (Harms) J. Léonard (Leguminosae-Caesalpinioideae-Detarieae) and its inclusion in Gilbertiodendron J. Léonard. S Afr J Bot 2012;78:257–265. [Google Scholar]
  • 40.Ngok Banak L, Breteler FJ. Novitates Gabonenses 50. The genus Oddoniodendron (Leguminosae, Caesalpinioideae) from Lower Guinea: a taxonomic revision with description of two new species from Gabon. Adansonia. 2004;26:241–250. [Google Scholar]
  • 41.Burgt XM van der, Eyakwe M, Motoh J. Gilbertiodendron newberyi (Leguminosae: Caesalpinioideae), a new tree species from Korup National Park, Cameroon. Kew Bulletin. 2012;67:51–57. [Google Scholar]
  • 42.Burgt XM van der, Mackinder BA, Wieringa JJ, Estrella M de la. The Gilbertiodendron ogoouense species complex (Leguminosae: Caesalpinioideae), Central Africa. Kew Bull. 2015;70:29. 10.1007/s12225-015-9579-4 [DOI] [Google Scholar]
  • 43.Wieringa JJ. Monopetalanthus Exit.: a Systematic Study of Aphanocalyx, Bikinia, Icuria, Michelsonia and Tetraberlinia (Leguminosae, Casalpinioideae [dissertation]. Wageningen University and Research ProQuest Dissertations Publishing, 1999. 28233563.
  • 44.Mackinder B. Tribe Detarieae. In: Lewis G, Schrire B, Mackinder B, Lock M, eds. Legumes of the world. Kew: Royal Botanic Gardens. 2005. p. 69–109. [Google Scholar]
  • 45.Radosavljevic A, Mackinder BA, Herendeen PS. Phylogeny of the detarioid legume genera Cynometra and Maniltoa. Sys Bot. 2017;42:1–10. [Google Scholar]
  • 46.Radosavljevic A. The rise of Cynometra (Leguminosae) and the fall of Maniltoa: a generic re-circumscription and the addition of 4 new species. PhytoKeys. 2019;127:1–37. doi: 10.3897/phytokeys.127.29817 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 47.Obembe OA. Structural variation of stomata in some dicotyledonous trees. Global J Biol, Agr & Hlth Sci. 2015;4:173–181. [Google Scholar]
  • 48.Breteler FJ. 2006. Novitates Gabonenses 56. Two Anthonomtha species from Gabon transferred to Englerodendron (Fabaceae, Caesalpinioideae). Adans 2006;28:105–111. [Google Scholar]
  • 49.Breteler FJ. Revision of the African genus Isomacrolobium (Leguminosae: Caesalpinioideae). Plant Ecol Evol. 2011;144:64–81. [Google Scholar]
  • 50.Estrella M de la, Wieringa JJ, Breteler FJ, Ojeda DI. Re-evaluation of the genus Englerodendron (Leguminosae–Detarioideae), including Isomacrolobium and Pseudomacrolobium. Australian Syst Bot. 2019;32:564–571. [Google Scholar]
  • 51.Ojeda DI, Koenen E, Cervantes S, Estrella M de la, Banguera-Hinestroza E, Janssens SB, et al. Phylogenomic analyses reveal an exceptionally high number of evolutionary shifts in a florally diverse clade of African legumes. Mol Phylogenet Evol. 2019;137:156–167. doi: 10.1016/j.ympev.2019.05.002 [DOI] [PubMed] [Google Scholar]
  • 52.Jongkind CCH, Breteler FJ. Englerodendron libassum (Leguminosae-Detarioideae-Amherstieae), a new critically endangered tree species from coastal Liberia. Plant Ecol Evol. 2020;153:487–491. [Google Scholar]
  • 53.Schulman L.; Junikka L.; Mndowla A.; Rajabu I. Trees of Amani Nature Reserve, NE Tanzania. Ministry of Natural Resources and Tourism. Helsinki: Helsinki University Printing House; 1998. [Google Scholar]
  • 54.Lovett JC, Ruffo CK, Gereau RE, Taplin JRD. Field guide to the moist forest trees of Tanzania. York (UK): York Publishing Services; 2006. [Google Scholar]
  • 55.Burgt XM van der, Eyakwe MB, Newbery DM. Englerodendron korupense (Fabaceae, Caesalpinioideae), a new tree species from Korup National Park, Cameroon. Adansonia. 2007;29:59–65. [Google Scholar]
  • 56.Tedersoo L, Brundrett MC. Evolution of ectomycorrhizal symbiosis in plants. Ecol Stud. 2017;230:407–467. [Google Scholar]
  • 57.Morley RJ. Origin and evolution of tropical rain forests. Chichester (UK): Wiley; 2000. [Google Scholar]
  • 58.Vincens A, Tiercelin J-J, Buchet G. New Oligocene–early Miocene microflora from the southwestern Turkana Basin: palaeoenvironmental implications in the northern Kenya Rift. Palaeogeogr, Palaeoclim, Palaeoecol. 2006;239:470–486. [Google Scholar]
  • 59.Romero IC, Kong S, Fowlkes CC, Jaramillo C, Urban MA, Oboh-Ikuenobe F, et al. Improving the taxonomy of fossil pollen using convolutional neural networks and superresolution microscopy. PNAS. 2020;117:28496–28505. doi: 10.1073/pnas.2007324117 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 60.Eggeling WJ. Observations on the ecology of the Budongo Rain Forest, Uganda. J Ecol. 1947;34:20–87. [Google Scholar]
  • 61.Poorter L, Bongers F, Kouamé FNG, Hawthorne WD. Biodiversity of West African forests: an ecological atlas of wood plant species. CABI:2004. e-book: https://cabidigitallibrary.org/doi/book/10.1079/9780851997346.0000
  • 62.Newbery DM, Burgt XM van der, Worbes M, Chuyong GB. Transient dominance in a central African rain forests. Ecol Monogr. 2013;83:339–382. [Google Scholar]
  • 63.Kearsley E, Verbeeck H, Hufkens K, Van de Perre F, Doetterl S, Baert G, et al. Functional community structure of African monodominant Gilbertiodendron dewevrei forest influenced by local environmental filtering. Ecol Evol. 2016;7:295–304. 10.1002/ece3.2589. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 64.Burgt XM van der. Co-dominant Detarioideae (Leguminosae) tree species in the rain forests of Korup National Park [dissertation]. Oxford (UK): Oxford Brookes University; 2018. [Google Scholar]
  • 65.Furuichi T, Hashimoto C, Tashiro Y. Fruit availability and habitat use by chimpanzees in the Kalinzu Forest, Uganda: examination of fallback foods. Int J Primatol. 2001;22:929–945. [Google Scholar]
  • 66.Pangou SV, Maury-Lechon G, Moutanda A. Monodominant forests of Aucoumea klaineana and Terminalia superba in the Chaillu Forest (SW Congo, Africa). Pol Bot J. 2003;48:145–162. [Google Scholar]
  • 67.Estrella M de la, Forest F, Wieringa JJ, Fougère-Danezan M, Bruneau A. Insights on the evolutionary origin of Detarioideae, a clade of ecologically dominant tropical African trees. New Phytol. 2017;214: 1722–1735. doi: 10.1111/nph.14523 [DOI] [PubMed] [Google Scholar]
  • 68.Duvall CS. Habitat, conservation, and use of Gilletiodendron glandulosum (Fabaceae, Caesalpinioideae) in southwestern Mali. Syst Geogr Plants. 2001;71:699–737. [Google Scholar]
  • 69.Diefendorf A.F., Mueller K.E., Wing S.L., Koch P.L., Freeman K.H., Global patterns in leaf C-13 discrimination and implications for studies of past and future climate. PNAS. 2010;107:5738–5743. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 70.Grímsson FG, Graham SA, Coiro M, Jacobs BF, Xafis A, Neumann FH, et al. Origin and divergence of Afro-Indian Picrodendraceae: linking pollen morphology, dispersal modes, fossil records, molecular dating and paleogeography. Grana 2019;58:227–275. doi: 10.1080/00173134.2019.1594357 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 71.Ulrich S, Grímsson F. The single-grain method: adding TEM to the equation. Grana 2020;59:44–57. doi: 10.1080/00173134.2019.1666915 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 72.Grímsson FG, Ulrich S, Coiro M, Graham SA, Jacobs BF, Currano ED, et al. Hagenia from the early Miocene of Ethiopia: Evidence for possible niche evolution. Ecology and Evolution 2021;11:5164–5186. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 73.White, F. The Vegetation of Africa, a Descriptive Memoir to Accompany the UNESCO/AETFAT/UNSO Vegetation Map of Africa (3 Plates, Northwestern Africa, Northeastern Africa, and Southern Africa, 1: 5,000,000). Paris (France): Unesco; 1983.
  • 74.Ferguson D.K. The origin of leaf-assemblages-new light on an old problem. Rev Pal Palynol. 1985;46:117–88. [Google Scholar]
  • 75.Spicer RA. The formation and interpretation of plant fossil assemblages. Adv Bot Res. 1989;16:96–191. [Google Scholar]
  • 76.Burnham R, Relationships between standing vegetation and leaf litter in a paratropical forest: implications for paleobotany. Rev Pal Palynol. 1989;58:5–32. [Google Scholar]
  • 77.Greenwood DR. The taphonomy of plant macrofossils. In: Donovan SK, editor. The Processes of Fossilization. New York: Columbia University Press; 1991.p. 141–169. [Google Scholar]
  • 78.Peh KS-H, Sonké B, Séné O, Djuikouo M-NK, Nguembou CK, Taedoumg H, et al. Mixed-forest species establishment in a monodominant forest in Central Africa: implications for tropical forest invasibility. PLOS One. 2014;9:e97585. 10.1371/journal.pone.0097585.g001. doi: [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 79.Jost L. Partitioning diversity into independent alpha and beta components. Ecology. 2007;88:2427–2439. doi: 10.1890/06-1736.1 [DOI] [PubMed] [Google Scholar]
  • 80.Currano E.D., Jacobs B.F., Pan A.D., Tabor N.J., Inferring ecological disturbance in the fossil record: a case study from the late Oligocene of Ethiopia. Palaeogeogr. Palaeoclimatol. Palaeoecol. 2011;309: 242–252. [Google Scholar]
  • 81.Torti SD, Coley PD. Tropical monodominance: a preliminary test of the ectomycorrhizal hypothesis. Biotropica. 1999;31:220–228. [Google Scholar]
  • 82.McGuire KL. Common ectomycorrhizal networks may maintain monodominance in a tropical rain forest. Ecol. 2007;88:567–574. [DOI] [PubMed] [Google Scholar]
  • 83.Thomas SC. Population densities and patterns of habitat use among anthropoid primates of the Ituri Forest, Zaïre. Biotropica. 1991;23:68–83. [Google Scholar]
  • 84.Gubista KR. Small mammals of the Ituri forest, Zaire: diversity and abundance in ecologically distinct habitats. J Mammal. 1999;80:252–262. [Google Scholar]
  • 85.Morgan D, Sanz C, Onononga JR, Strindberg S. Ape abundance and habitat use in the Goualougo Triangle, Republic of Congo. Int J Primatol. 2006;27:147–179. [Google Scholar]
  • 86.Mockrin MH, Rockwell RF, Redford KH, Keuler NS. Effects of landscape features on the distribution and sustainability of ungulate hunting in northern Congo. Cons Biol. 2011;25:514–525. doi: 10.1111/j.1523-1739.2011.01660.x [DOI] [PubMed] [Google Scholar]
  • 87.Devos C, Sanz C, Morgan D, Onononga J-R, Laporte N, Huynen M-C. Comparing ape densities and habitats in northern Congo: surveys of sympatric gorillas and chimpanzees in Odzala and Ndoki Regions. Amer J Primatol. 2008;70:1–13. [DOI] [PubMed] [Google Scholar]
  • 88.Breuer T, Breuer-Ndoundou Hockemba M, Strinderg S. Small-scale dung survey reveals high forest elephant density and preference for mixed species forest in an intact protected area. Biodivers Conserv. 2021: 10.1007/s10531-021-02214-7. [DOI] [Google Scholar]
  • 89.Melletti M, Mirabile M, Penteriani V, Boitani L. Habitat use by forest mammals in Dzanga-Ndoki National Park, Central African Republic. Afr J Ecol. 2009;47:797–800. [Google Scholar]
  • 90.Kurten EL, Carson WP. Do ground-dwelling vertebrates promote diversity in a Neotropical forest? Results from a long-term exclosure experiment. BioSci. 2015;65:862–870. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 91.Sheil D, Salim A. Forest tree persistence, elephants, and stem scars. Biotropica. 2004;36:505–521. [Google Scholar]
  • 92.Swaine MD, Hall JB. The monospecific tropical forest of Ghanaian endemic tree Talbotiella gentii. In: Synge H, editor. The biological aspects of rare plant conservation. London (UK): J. Wiley; 1981. p. 355–363. [Google Scholar]
  • 93.Voorhoeve AG. Some notes on the tropical rainforest of the Yoma-Gola National Forest near Bomi Hills, Liberia. Commonwealth For Rev. 1964;43:17–24. [Google Scholar]
  • 94.van Rooyen M, van Rooyen N, Orban B, Nsongola G, Miabangana ES, Gaugris J. Floristic composition, diversity and structure of the forest communities in the Kouilou Département, Republic of Congo. Trop Ecol. 2016;57:805–824. [Google Scholar]
  • 95.Nik Norafida NA, Nizam MS, Wan Juliana WA, Faezah P. Species richness and floristic variation of tree communities in Dryobalanops aromatica Gaertn. f. dominated forests of Peninsular Malaysia. Malayan Nature J. 2018;70:323–331. [Google Scholar]
  • 96.Appanah S, Turnbull JM. A review of dipterocarps: taxonomy, ecology and silviculture. Bogor (Indonesia): Center for International Forestry Research; 1998. [Google Scholar]
  • 97.Yamada I. Tropical rain forests of Southeast Asia: a forest ecologist’s view (Monographs of the Center for Southeast Asian Studies, Kyoto University). Manoa: University of Hawaii Press; 1997. [Google Scholar]
  • 98.Kondo T, Otani T, Lee SL, Tani N. Pollination system of Shorea curtisii, a dominant species in hill dipterocarp forests. J Trop For Sci. 2016;28:318–323. [Google Scholar]
  • 99.Haryati JR, Azizah IN, Arisoesilaningsih E. Eusideroxylon zwageri (Ulin) as key species in two zones of Sangkima Rain Forest, Kutai National Park, East Kalimantan. J Trop Life Sci. 2011;11: 47–50. [Google Scholar]
  • 100.Gamble JS. Gutta Percha trees of the Malay Peninsula. Bull. Misc. Inform. Kew: Royal Botanic Gardens, Kew;1907: 109–121. [Google Scholar]
  • 101.Anbarashan M, Parthasarathy N. Tree diversity of tropical dry evergreen forests dominated by single or mixed species on the Coromandel coast of India. Trop Ecol. 2013;54:179–190. [Google Scholar]
  • 102.Rahman MM, Nishat A, Rahman GMM, Ruprecht H, Vacik H. Analysis of spatial diversity of sal (Shorea robusta Gaertn. F) forests using neighbourhood-based measurements. Comm Ecol. 2008;9:193–199. [Google Scholar]
  • 103.Lamotte S, Gajaseni J and Malaisse F. Structure diversity in three forest types of north-eastern Thailand (Sakaerat Reserve, Pak Tong Chai). Biotechnology, Agronomy and Society and Environment. 1998;2:192–202. [Google Scholar]
  • 104.Bradford M, Murphy HT. The importance of large-diameter trees in the wet tropical rainforests of Australia. PLoS One. 2019;14(5): e028377. doi: 10.1371/journal.pone.0208377 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 105.Martijena NE, Bullock SH. Monospecific dominance of a tropical deciduous forest in México. J Biogeogr. 1994;21:63–74. [Google Scholar]
  • 106.Boucher DH. Seed predation by mammals and forest dominance by Quercus oleoides, a tropical lowland oak. Oecologia. 1981;49:409–414. [DOI] [PubMed] [Google Scholar]
  • 107.Craig RJ. Ecological characteristics of a native limestone forest on Saipan, Mariana Islands. Micronesica. 1992;25:85–97. [Google Scholar]
  • 108.Mueller-Dombois D, Jacobi JD, Boehmer HJ. `Ohi`a lehua rainforest: born among Hawaiian volcanoes, Evolved in Isolation: the story of a dynamic ecosystem with relevance to forests worldwide. Manoa (HI): Friends of the Joseph Rock Herbarium; 2013. [Google Scholar]
  • 109.Anderson AB. Use and management of native forests dominated by Açaí palm (Euterpe oleracea Mart.) in the Amazon estuary. Adv Econ Bot. 1988;6:144–154. [Google Scholar]
  • 110.Ragsac AC, Farias-Singer R, Freitas LB, Lohmann LG, Olmstead RG. Phylogeny of the Neotropical tribe Jacarandeae (Bignoniaceae). Am J Bot. 2020;106:1589–1601. [DOI] [PubMed] [Google Scholar]
  • 111.Degagne RS, Henkel TW, Steinberg SJ, Fox L III. Identifying Dicymbe corymbosa monodominant forests in Guyana using satellite imagery. Biotropica. 2009;41:7–15. [Google Scholar]
  • 112.Nascimento MT, Barbosa RI, Dexter KG, de Castilho CV, da Silva Carvalho C. Is the Peltogyne gracilipes monodominant forest characterized by distinct soils? Acta Oecologica. 2017;85:104–107. [Google Scholar]
  • 113.Condit R, Hubbell SP, Foster RB. Mortality and growth of a commercial hardwood ‘el cativo’, Prioria copaifera, in Panama. Forest Ecology and Management 1993;62:107–122. [Google Scholar]
  • 114.Fonty E, Molino J-F, Prévost M-F, Sabatier D. A new case of neotropical monodominant forest: Spirotropis longifolia (Leguminosae-Papilionoideae) in French Guiana. J Trop Ecol. 2011;27:641–644. [Google Scholar]
  • 115.Dantas AR, Guedes MC, de Cruz Vasconcelos C, Isacksson JGL, Pastana DNB, Lira-Guedes AC, et al. Morphology, germination, and geographic distribution of Pentaclethra macroloba (Fabaceae): a hyperdominant Amazonian tree. Rev Biol Trop. 2021;69:181–196. [Google Scholar]
  • 116.Barnett AA, Boye SA, Kinap NM, dos Santos-Barnett TC, Camilo TT, Parolin P, et al. Buds, bugs and bienniality: the floral biology of Eschweilera tenuifolia (O. Berg) Miers in a black-water flooded forest, central Amazonia. Forest. 2020;11:1–28. [Google Scholar]

Decision Letter 0

Gongle Shi

28 Oct 2022

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Reviewer #2: Yes

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Reviewer #1: This manuscript describes an exciting association of fossil leaflets of Englerodendron mulugeta sp. nov., from the Early Miocene of Ethiopia. The work is important for providing evidence of a monodominant tropical moist forest. I applaud the authors for compiling large and valuable images/datasets of cuticular and pollen information. I particularly like the quality of the SEM images of the pollen.

I have carefully reviewed the manuscript (see marked pdf), and here I provide some points:

The tiff files of figures 1 & 2 I was able to download are not of the best resolution. I had difficulty seeing some characters mentioned in the diagnosis and detailed description. I also would like to see additional closeups of some of the leaflets (e.g., twisted pulvinus, secondary and higher order venation.) Since this is the flora's most dominant taxon, there should be plenty of images. It looks like this "Legume 1 = Englerodendron mulugeta sp. nov" has been informally described/figured in other articles. However, the reader of this paper should see all the relevant images given that a new species is being erected.

The images of the fossil cuticles of the new species appear blurry in the Tiff file. Please consider new photos of the fossil cuticles at 10um to facilitate the comparisons with living taxa.

I have a few concerns regarding the monodominance of the forest, and I like that the authors stated, "it is possible that the forest at the time of Level A was on its way to monodominance". Although the percentages of the fossil leaflets are relatively large, they don't appear to be entirely the dominant taxon when compared with the few data available from tropical Africa (Table 3, Peh mono1-3). Considering that the leaflets were counted as leaves needs additional treatment in the statistical analyses.

It would be nice if the coauthors added a new figure plotting "Percent Dominant Taxon" against the stratigraphic levels.

Reviewer #2: This manuscript describes Englerodendron mulugeta sp. nov., a Detarioid legume from the early Miocene of Ethiopia based on abundant leaflets recovered from the Mush Valley site. The authors compare the fossil leaves with extant species of Detarioideae to support their taxonomic assessment and provide evidence of fossilized pollen that may correspond to the same or closely related species. The high abundance of leaves and pollen throughout the 50–60kyr sequence of the Mush Valley site are interpreted as evidence of a monodominant forest community dominated by a tree species belonging to a linage in which ecological dominants are common.

The manuscript is clear, the methodology is sound and the results are well-supported. I recommend this paper for publication. There are only three minor suggestions that I consider the authors should address:

1. Please revise the international code of botanical nomenclature for correct epithet assignation. Is ‘mulugeta’ treated as a latinized noun in apposition? The reference that the authors provide for this epithet is “he who rules”, which sounds more like an adjective instead. If this is the case (adjective), the adequate spelling should be “mulugetum”. If naming in honor of Dr. Mulugeta Fesesha it should be “mulugetanum”.

2. Figure 1 – The quality of images is quite poor and therefore the species description and morphological comparisons are hard to follow. The little detail that was visible is consistent with the species description, but I suggest that the authors include better images and/or consider including an illustration of the type specimen. Particularly the fine venation is impossible to figure out.

3. Even though the authors include a Table with detailed morphological comparison between the fossils and living species of Detarioideae, I encourage the authors to include a supplementary figure with leaves of the species they compared the fossils with, as a means to provide stronger evidence for their taxonomic assessment.

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Reviewer #2: No

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Attachment

Submitted filename: PONE-D-22-26695_reviewer.pdf

PLoS One. 2023 Jan 11;18(1):e0279491. doi: 10.1371/journal.pone.0279491.r002

Author response to Decision Letter 0


6 Nov 2022

Dr. Gongle Shi, Academic Editor, and Reviewer 1 and Reviewer 2:

Thank you very much for your review of our manuscript [PONE-D-22-26695]: First evidence of a monodominant (Englerodendron, Amherstieae, Detarioideae, Leguminosae) tropical moist forest from the early Miocene (21.73 Ma) of Ethiopia, on behalf of PLOS ONE. We appreciate the opportunity to submit the minor revision of our paper for your consideration. Below we respond to the editor’s and reviewers’ comments and note corresponding changes we have made in our paper.

We have reviewed our revised manuscript to make sure that it meets PLOS ONE’s style requirements. We have included a completed copy of PLOS’ questionnaire on inclusivity in global research with the revised manuscript and have included it in Supporting Information as S1. We have included our full ethics statement in the Methods section.

PLOS ONE and the academic editor had some concern about Figure 6, now Figure 7 in the revised manuscript, and that it might copyrighted. This figure was created solely using Simplemappr, which is in the public domain (similar to USGS National Map Viewer, The Gateway to Astronaut Photography of Earth, etc.) and which we have seen used in other article published by PLOS ONE. The following language is included on the website: “All versions of SimpleMappr map data found on this website are in the Public Domain. You may use the maps in any manner, including modifying the content and design, electronic dissemination, and offset printing. The primary author, David P. Shorthouse has waived all copyright, related or neighboring rights, and financial claim to the maps and invites you to use them for personal, educational, and commercial purposes. No permission is needed to use SimpleMappr. Crediting the author is unnecessary.” (https://www.simplemappr.net/#tabs=6). In the figure legend we have included the following language, “This map was created with Simplemappr (https://www.simplemappr.net/).”

We have included the language required for new species in a “Nomenclature” sub-section in the Methods section as required by PLOS ONE. In addition, we have changed all ‘Fabaceae’ to ‘Leguminosae’ for consistency. In addition, small grammatical or punctuation errors that we have found in the course of this revision have been corrected.

We have reviewed the reference section and have made no changes. We have updated some information in the Supporting Information to provide additional images as requested by Reviewer 2.

Below you will find our responses to the comments and concerns of Reviewer 1 and Reviewer 2:

Reviewer 1 (R1) concern:

“The tiff files of figures 1 &2 I was able to download are not of the best resolution. I had difficulty seeing some characters mentioned in the diagnosis and detailed description. I would also like to see additional closeups of some of the leaflets (e.g., twisted pulvinus, secondary and higher order venation.) Since this is the flora’s most dominant taxon, there should be plenty of images. It looks like this “Legume 1 – Englerodendron mulugeta sp. nov.” has been informally described/figured in other articles. However, the reader of this paper should see all the relevant images given that a new species is being erected.”

Authors’ Response:

We have redone Fig 1 and have made an additional figure (which is now Fig 2) so that the characters in the diagnosis and description can be more easily seen. This includes high resolution and larger images of the fossil species, as well as extant species. We have specifically added an image of MU29-41 #4 (Figure 2C), which has very good details of the canaliculate midvein, and the secondary, tertiary, and quaternary venation. 5th level venation of the taxon can be observed in Figure 3F of Bush et al. (2017). In addition, in the Supporting information we have provided images of 4 more specimens that provide additional viewing of the characteristics noted in the manuscript.

Reviewer 1 (R1) concern:

“The images of the fossil cuticles of the new species appear blurry in the Tiff file. Please consider new photos of the fossil cuticles at 10 μm to facilitate the comparisons with living taxa.”

Authors’ Response:

We have selected new images of the fossil cuticle and have made sure that the resolution is at 300 dpi.

Reviewer 1 (R1) concern:

“I have a few concerns regarding the monodominance of the forest, and I like that the authors stated, “it is possible that the forest at the time of Level A was on its ways to monodominance”. Although the percentages of the fossil leaflets are relatively large, they don’t appear to be entirely the dominant taxon when compared with the few data available from tropical Africa (Table 3, Peh mono 1-3). Considering that the leaflets were counted as leaves needs additional treatment in the statistical analyses.”

Authors’ Response:

The dominance of the fossil Englerodendron in the Mush plant assemblages is particularly notable, not only in terms of the abundance of the morphotype/taxon in Levels B - F, and prevalence in Level A, but also in representing the most abundant taxon at around 5 – 6.5 times (excluding Level A, which is 3 times) the level of the next most abundant species over a duration of tens of thousands of years. The taxon does not appear to be a short-term proliferating species that has been sampled in a single large stratum in abundance, but in multiple levels, likely showing an estimated 40,000 – 50,000 years of dominance. In regards to comparisons with Peh et al.’s (2012) study, we believe that it is valid. The dominant species in his work is Gilbertiodendron dewevrei, which is also a paripinnate-compound leaved legume species in the Berlinia Clade. Gilbertiodendron dewevrei, is typically 3-jugate, so each leaf usually consists of 6 leaflets. In the leaf litter fall studies whole and partial leaves (including leaflets) are used in litterfall weighing. In addition, the new fossil Englerodendron species is not the only compound-leaved legume in the flora, with the next two taxa (‘Short-drip tip’ and ‘Interrupt’) each making up 4 – 10% of the material in each level, but never to the extent of the fossil Englerodendron species. Conversely, other taxa present in the fossil flora, Newtonia mushensis (Pan et al. 2012) and Zanthoxylum sp., are only represented as fruits and seeds. Both genera, Newtonia (Leguminosae: Mimoseae) and Zanthoxylum (Rutaceae), are noted for possessing diagnostic leaves (with diagnostic leaflets) that are pinnately-compound. No potential candidates representing either of these genera have been found amongst the fossil leaf(let) material from Mush. We believe the statistical analyses in which we have used Hill numbers for Mush and Chilga (Guang and Bull’s Bellow) provide evidence for the presence of monodominance of Englerodendron at Mush. We also note that the dominant taxa at Chilga are Cynometra chaka (Guang) and an Albizia-like legume leaf type (Bull's Bellow), both of which have compound leaves.

Reviewer 1 (R1) concern:

“It would be nice if the coauthors added a new figure plotting “Percent Dominant Taxon” against the stratigraphic levels.”

Authors’ Response:

We have added a bar graph figure, Fig 8, which shows percent of abundance of the fossil Englerodendron leaflets plotted against stratigraphic height. In addition, similar bar plots for abundances of the taxa can be found in Currano et al. (2020) as Figure 6.

In addition, we have made almost all of the recommended changes that Reviewer 1 (R1) noted in the manuscript. We have kept the description of some of the petioles as ‘terete’ instead of ‘interpreted or likely terete’ as suggested by R1, because some of the fossils, particularly as seen in Fig 2A and S5, show straight pulvinate petioles indicating the presence of this characteristic, along with some specimens possessing twisted pulvinate petiolules in the fossil Englerodendron species.

Reviewer 2 (R2) concern:

“1. Please revise the international code of botanical nomenclature for correct epithet assignation. Is ‘mulugeta’ treated as a latinized noun in apposition? The reference that the authors provide for this epithet is “he who rules”, which sounds more like an adjective instead. If this is the case (adjective), the adequate spelling should be “mulugetum”. If naming in honor of Dr. Mulugeta Fesesha it should be “mulugetanum”.”

Authors’ Response:

We fully agree and thank R2 for informing us on this issue. We have changed the proposed species name to Englerodendron mulugetanum and have changed the etymology section accordingly.

Reviewer 2 (R2) concern:

“2. Figure 1 – The quality of images is quite poor and therefore the species description and morphological comparisons are hard to follow. The little detail that was visible is consistent with the species description, but I suggest that the authors include better images and/or consider including an illustration of the type specimen. Particularly the fine venation is impossible to figure out.”

Authors’ Response:

This is similar to the concerns of R1 and we have changed the images accordingly to make sure that we have provided images to assist the reader in recognizing and viewing the characteristics of the new species. We have redone Fig 1 and added another figure (now Fig 2) so that the characters in the diagnosis and description can be determined more easily, including high resolution images of the fossil and extant species. Specimen MU29-41 #4 (Figure 2C) has been added and provides very good details of the canaliculate midvein, and the secondary, tertiary, and quaternary venation. 5th level venation of the taxon can be observed in Figure 3F of Bush et al. (2017). We have also provided images of 4 additional specimens in Supporting information.

Reviewer 2 (R2) concern:

“3. Even though the authors include a Table with detailed morphological comparison between the fossils and living species of Detarioideae, I encourage the authors to include a supplementary figure with leaves of the species they compared the fossils with, as a means to provide stronger evidence for their taxonomic assessment.”

Authors’ Response:

We have created an additional document in Supporting Information that includes a number of examples of other Amherstieae leaf(let) images and characteristics to assist the reader. This was a very good idea. Thank you!

Again, we want to thank the academic editor and the 2 reviewers for very helpful suggestions to assist in making this a better paper. If you have any additional questions or need more information, please let us know. Thank you again for consideration of our revised manuscript.

Kind regards,

Aaron D. Pan, Ph.D.

Executive Director

Museum of Texas Tech University

Texas Tech University

Attachment

Submitted filename: Rebuttal letter.docx

Decision Letter 1

Gongle Shi

8 Dec 2022

FIRST EVIDENCE OF A MONODOMINANT (ENGLERODENDRON, AMHERSTIEAE, DETARIOIDEAE, LEGUMINOSAE) TROPICAL MOIST FOREST FROM THE EARLY MIOCENE (21.73 MA) OF ETHIOPIA

PONE-D-22-26695R1

Dear Dr. Pan,

We’re pleased to inform you that your manuscript has been judged scientifically suitable for publication and will be formally accepted for publication once it meets all outstanding technical requirements.

Within one week, you’ll receive an e-mail detailing the required amendments. When these have been addressed, you’ll receive a formal acceptance letter and your manuscript will be scheduled for publication.

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If your institution or institutions have a press office, please notify them about your upcoming paper to help maximize its impact. If they’ll be preparing press materials, please inform our press team as soon as possible -- no later than 48 hours after receiving the formal acceptance. Your manuscript will remain under strict press embargo until 2 pm Eastern Time on the date of publication. For more information, please contact onepress@plos.org.

Kind regards,

Gongle Shi, Ph.D.

Academic Editor

PLOS ONE

Additional Editor Comments (optional):

Reviewers' comments:

Acceptance letter

Gongle Shi

14 Dec 2022

PONE-D-22-26695R1

First evidence of a monodominant (Englerodendron, Amherstieae, Detarioideae, Leguminosae) tropical moist forest from the early Miocene (21.73 Ma) of Ethiopia

Dear Dr. Pan:

I'm pleased to inform you that your manuscript has been deemed suitable for publication in PLOS ONE. Congratulations! Your manuscript is now with our production department.

If your institution or institutions have a press office, please let them know about your upcoming paper now to help maximize its impact. If they'll be preparing press materials, please inform our press team within the next 48 hours. Your manuscript will remain under strict press embargo until 2 pm Eastern Time on the date of publication. For more information please contact onepress@plos.org.

If we can help with anything else, please email us at plosone@plos.org.

Thank you for submitting your work to PLOS ONE and supporting open access.

Kind regards,

PLOS ONE Editorial Office Staff

on behalf of

Dr. Gongle Shi

Academic Editor

PLOS ONE

Associated Data

    This section collects any data citations, data availability statements, or supplementary materials included in this article.

    Supplementary Materials

    S1 File. Inclusivity in global research information and checklist.

    (DOCX)

    S2 File. Herbarium specimens examined.

    (XLSX)

    S3 File. Herbarium specimens sampled for micro-morphological (leaf cuticle) and palynological analysis.

    (XLSX)

    S4 File. Additional Englerodendron mulugetanum sp. nov. specimens.

    (PDF)

    S5 File. Table of comparing African Amherstieae (Leguminosae, Detarioideae) leaf and leaflet characteristics.

    (XLSX)

    S6 File. African Amherstieae (Leguminosae, Detarioideae) leaf and leaflet images and characteristics.

    (PDF)

    S7 File. Abaxial and adaxial leaf cuticle images of Berlinia Clade (Leguminosae, Detarioideae, Amherstieae) taxa.

    (PDF)

    Attachment

    Submitted filename: PONE-D-22-26695_reviewer.pdf

    Attachment

    Submitted filename: Rebuttal letter.docx

    Data Availability Statement

    All relevant data are within the paper and its Supporting Information files.


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