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Milicia excelsa

Milicia excelsa (Welw.) C.C.Berg is a large or semi-evergreen belonging to the family, endemic to the tropical lowlands of and renowned for its durable, golden-brown timber commercially known as or African teak. It typically attains heights of 30–50 meters with trunk diameters exceeding 1 meter, supported by prominent buttresses and crowned by dense, spreading foliage of elliptic, dark green leaves. The produces small, unisexual flowers in separate inflorescences and figs containing seeds dispersed by various vertebrates. Native to a broad swath of tropical Africa from and in the west to and in the east, and extending south to , , and , M. excelsa thrives in forests, gallery woodlands, and forest-savanna mosaics, often on well-drained, fertile soils at elevations up to 1,200 meters. It serves as an species, enhancing through leaf litter and providing shade for crops, while its timber—resistant to and fungi—is extensively harvested for , furniture, boat-building, and veneer production. Various plant parts, including bark and roots, are utilized in to treat ailments such as infections, rheumatism, and gastrointestinal disorders. Despite its wide distribution, M. excelsa faces pressures from , agricultural expansion, and intensive , leading to its classification as Near Threatened on the , with populations declining in many regions due to unsustainable exploitation. efforts emphasize sustainable practices and protected areas to mitigate these threats and preserve its ecological role in maintaining forest structure and .

Taxonomy and morphology

Taxonomic classification

Milicia excelsa is classified in the domain Eukaryota, kingdom Plantae, phylum Tracheophyta, class Magnoliopsida, order , family , genus , and species M. excelsa. The binomial name (Welw.) C.C.Berg reflects its transfer from the former genus Chlorophora to Milicia, established by Cornelis C. Berg in based on morphological distinctions in inflorescence structure and fruit characteristics separating the two genera within .
RankName
DomainEukaryota
KingdomPlantae
PhylumTracheophyta
ClassMagnoliopsida
OrderRosales
FamilyMoraceae
GenusMilicia
SpeciesMilicia excelsa
The basionym is Chlorophora excelsa Welw., published by Friedrich Welwitsch in 1859 from specimens collected in Angola, with subsequent synonyms including Chlorophora alba A.Chev. and Chlorophora excelsa (Welw.) Benth. & Hook.f. These synonyms arose from earlier classifications grouping it with fig-like trees in Chlorophora before phylogenetic and anatomical revisions confirmed Milicia as distinct, supported by pollen morphology and latex properties unique to the genus. Placement in Moraceae aligns with shared traits such as milky latex, unisexual flowers, and syconium-like inflorescences, though Milicia species exhibit drupaceous fruits differing from Ficus figs. No subspecies are currently recognized, though genetic studies indicate intraspecific variation across its African range.

Physical description

Milicia excelsa is a large tree attaining heights of 30–50 meters and bole diameters of 2–10 meters. The trunk is typically straight, buttressed at the base, and clear of branches for at least 20 meters above ground. The bark is thick, pale gray to brown, rough-textured, and flakes off in irregular squarish scales; it exudes a milky when cut. The crown is wide-spreading and flat-topped, formed by heavy branches that may ascend or extend horizontally. Leaves are simple, alternate, elliptic to oblong in shape, measuring 6–15 cm long and 3–7 cm wide, with an acuminate tip and dark green upper surface; they feature 10–22 pairs of lateral veins and are short-pubescent on the lower surface between the finer veins. are catkin-like , with male 3–5 cm long and female shorter; fruits are small, drupes approximately 2.5–3 mm in length.

Distribution and habitat

Geographic distribution

Milicia excelsa is native to tropical , with its range extending from in the west across to in the east, and southward to , , and . This distribution encompasses a broad swath of lowland and semi-evergreen forests in , Central, and , where it occurs in countries including , , , , , , , , , , , Côte d'Ivoire, , , , , , , , , , , , and . The species is absent from the regions and higher-altitude montane forests, preferring elevations generally below 1,000 meters, though recorded up to 1,350 meters in parts of its eastern range. While primarily wild-distributed, limited has occurred outside its native range for timber production, though such introductions remain localized and not naturalized.

Habitat preferences

Milicia excelsa primarily inhabits , , or forests, both primary and secondary, across tropical , showing a marked preference for drier forest types over consistently wet formations. It often functions as a secondary or in disturbed or regenerating areas, adapting to gaps in zones where it benefits from increased light availability. The species occurs at low to medium elevations, from up to 1,600 meters, though it is most common below 1,200 meters and rare at higher altitudes such as 4,500 meters on . It thrives in lowland moist forests, wet savannas, and coastal woodlands but avoids waterlogged sites, requiring well-drained conditions to prevent root issues. Soil preferences favor relatively fertile, well-aerated substrates, serving as an indicator of productive land suitable for ; it performs poorly on impeded or heavy clays. Optimal growth occurs in soils with 6.0–7.0 and textures supporting , such as sandy loams, under rainfall regimes of 100–2,200 mm annually, reflecting its tolerance for variable but predominantly tropical moist climates. The tree demonstrates broad edaphic adaptability across climatic zones from Guineo-Congolian to Sudanian-Guinean, though densities decline in excessively arid or flooded extremes.

Ecology

Reproductive biology

Milicia excelsa is dioecious, with separate and trees bearing unisexual inflorescences in catkins. Flowering occurs annually but asynchronously among individuals, with male trees typically blooming from late to early and female trees from early January to early in West African populations; peaks shift to for males and for females in Central African sites like . Flowering initiation correlates with prior decreases in minimum and relative , and individual trees maintain consistent earliness or lateness, suggesting genetic control; early-flowering females produce more seeds than late-flowering ones. Trees begin reproducing at approximately 25–30 years of age, with a observed female-to-male of about 2:1. Pollination is anemophilous, mediated by wind, enabling extensive dispersal over distances that reduce fine-scale spatial genetic in low-density populations. It often coincides with the leafless period (), potentially enhancing flow. The species exhibits an allogamous breeding system, with temporal isolation by flowering time (isolation by time) contributing to among trees separated by less than 1.7 km if their bloom differences exceed 20 days. Fruits mature 5–6 weeks after fertilization, with production varying yearly—not all trees fruit annually, though prolific years yield high outputs, such as 333,333–500,000 seeds per kg in some individuals. Seeds have a 1000-seed weight of 1–4 g and exhibit high rates (>90%) within 4 weeks if sown fresh, but viability declines rapidly, necessitating planting within 3 months; follows 2–4 weeks after . Dispersal is primarily zoochorous, with fruits initially falling beneath parent trees but removed by birds, bats (notably Eidolon helvum, which processes ripe fruits via gut passage to boost to 93.9% versus 45–47% for unprocessed seeds), squirrels, and other mammals; late-season disperser activity may offset disadvantages for late-flowering trees. This animal-mediated dispersal, combined with wind , supports broad despite the ' patchy distribution.

Ecological interactions

Milicia excelsa, a dioecious , relies on wind for , which typically occurs during the leafless period from to , facilitating transfer between male and female trees in low-density populations. Genetic analyses confirm extensive dispersal over wide distances, supporting despite the tree's sparse distribution in tropical forests. Seed dispersal is primarily mediated by vertebrates that consume the small, drupe-like fruits, which mature 5-6 weeks post-fertilization and are available from October to December. Key dispersers include birds, bats such as Eidolon helvum, and squirrels, which ingest the fruits and deposit seeds via , enabling secondary dispersal away from parent trees. Phenological studies reveal that fruiting synchrony and animal feeding strategies interact to influence dispersal efficiency, with isolation by time potentially limiting interactions in some populations. While specific pressures on foliage or are not extensively documented, the tree's natural against suggests limited fungal in living tissues, though post-harvest wood resists microbial degradation due to . In forest ecosystems, M. excelsa exhibits mutualistic associations with dispersers that enhance its , contributing to its persistence as a canopy emergent despite selective pressures.

Role in ecosystems

Milicia excelsa functions as a key upper-canopy species in and forests across West and , contributing to structural complexity and vertical stratification within these habitats. As a tree, it often emerges in gaps or disturbed areas, facilitating by providing shade and microhabitat conditions that support regeneration. The species' extensive buttressed roots and deep system enhance stability, particularly in riverine and lowland environments prone to , thereby maintaining integrity and preventing runoff into adjacent water bodies. Leaf litter from M. excelsa decomposes to enrich , promoting nutrient cycling and fertility for associated , as evidenced in trials where it positively influences crop yields through improved soil conditions. In mixed plantations, M. excelsa integrates with to bolster , creating heterogeneous canopies that harbor epiphytes, , and vertebrates while moderating local climate through and windbreaks. Its presence in efforts underscores a facilitative role in second-growth recovery, where it accelerates accumulation and carbon storage relative to monocultures.

Human uses

Timber and commercial applications

Milicia excelsa, commonly known as iroko, yields a hardwood prized for its durability and versatility in commercial applications. The wood exhibits medium weight with a density ranging from 550 to 750 kg/m³ at 12% moisture content, contributing to its strength comparable to teak in certain properties, though it is weaker in bending and compression along the grain. It possesses a Janka hardness of 1,260 lbf (5,310 N), rendering it resistant to wear and impact. The heartwood displays high natural durability against fungi, dry-wood borers, termites, and rot, with a durability index rated as very high (class 1-2 on standard scales). In construction, iroko timber is extensively used for structural elements, exterior cladding, decking, pergolas, and due to its resistance to moisture and insects, often serving as a substitute. Its workable qualities include good nailing, screwing, mortising, gluing, and turning, though it requires filler for optimal finishing and contains stilbenes that may cause irritation during processing. For interior applications, it finds employment in , paneling, , and furniture, where its golden to medium brown color and medium to coarse texture enhance aesthetic appeal while providing load-bearing capacity and resistance. Commercial harvesting targets reaching 30–48 m in height and up to 150 cm in diameter, yielding logs of 9–24 m lengths suitable for export and processing. As one of Africa's most valuable timbers, supports regional economies through demand in and industries, though overexploitation has prompted considerations in source regions.

Medicinal and traditional uses

In , Milicia excelsa (commonly known as or African teak) is utilized across tropical regions for treating diverse ailments, with ethnobotanical surveys in documenting its application in addressing 45 human diseases. The leaves, , roots, and are the primary parts employed, comprising 30.3% leaves, 25.8% , and 23.6% roots in reported uses. Leaf preparations are applied externally for snakebites, fever, and via , while internal decoctions target respiratory issues such as and , as well as , oedema, , lumbago, spleen disorders, and heart conditions. Root and stem bark decoctions are taken for female sterility, amenorrhea, and gastric obstructions, with preliminary pharmacological studies confirming effects in animal models and properties aligning with traditional applications for inflammatory conditions. Latex from the tree serves as an and is used to alleviate and obstructions, while exhibits effects. Additional ethnomedical reports from Côte d'Ivoire highlight its role in due to iron content in certain preparations. extracts of leaves have shown potential in mitigating anxiety- and depression-like behaviors in preclinical assays, supporting and anti-stress claims in traditional . These uses reflect cultural reliance on the , though remains largely anecdotal or preliminary, with no large-scale clinical validation.

Agroforestry and ornamental roles

Milicia excelsa is incorporated into traditional agroforestry systems across West Africa, particularly in regions like Benin and Nigeria, where farmers retain and protect mature trees on farmlands to leverage their contributions to soil fertility and ecosystem stability. These practices often involve conserving large old trees amid agricultural landscapes, which serve as refuges for the species amid broader deforestation pressures, while providing shade for crops and livestock. The tree's deep root system and nitrogen-fixing associations further support soil conservation and nutrient cycling in mixed farming setups. As a , Milicia excelsa is favored in multi-species agroforestry plantations for its ability to improve conditions and facilitate understory crop growth, with studies in humid tropical zones demonstrating enhanced survival when planted during long rainy seasons alongside compatible . Such systems also aid in the of , as evidenced by efforts in Côte d'Ivoire where plots maintain viable populations threatened by elsewhere. In ornamental contexts, Milicia excelsa is planted as a and boundary in rural and semi-urban settings, valued for its majestic stature reaching up to 50 meters and broad canopy. In , it demarcates farm or village borders, combining aesthetic appeal with practical utility in low-rainfall areas down to 700 mm annually. Its durable form makes it suitable for roadside and plantings, though susceptibility to pests like gall-forming limits widespread adoption without targeted .

Conservation status

Milicia excelsa is assessed as Near Threatened on the , with an ongoing decline in populations attributed to unsustainable harvesting and degradation across its in tropical . The species remains relatively common in some areas but faces heavy exploitation for high-value timber, leading to reduced densities in natural forests. In specific regions such as southern , populations have declined significantly, classifying the species as endangered locally due to exceeding regeneration capacity. Primary threats include selective and commercial timber extraction, which target mature trees and disrupt regeneration. Habitat loss from , , and land conversion for human activities further fragments populations and reduces suitable and habitats. Projections indicate potential shifts in suitable habitats due to , exacerbating vulnerability in already pressured areas. An additional biological threat is the gall-forming psyllid Phytolyma fusca, which infests seedlings and young trees, causing that stunt growth and increase mortality, severely hindering natural and propagation efforts. This has contributed to failures in initiatives and limits in disturbed sites. While natural regeneration occurs in open areas post-clearance, overall population recovery is impeded without targeted management.

Management strategies

Management strategies for Milicia excelsa emphasize due to the species' low within populations but high variation between them, necessitating protection of multiple populations across its range to preserve overall genetic resources. Integrated approaches in combine ecological assessments, morphological and genetic studies of remnant populations, and targeted interventions to sustain viable stands, particularly in fragmented habitats like those in . Traditional practices play a central role, with local communities in venerating the tree as a conservatory of cultural values and embodiment of divinities, leading to its protection on farms, in sacred groves, and public spaces; these customs have proven effective for by restricting felling without communal rituals. efforts leverage such ethnobotanical knowledge, integrating it with formal protections to enhance compliance and reduce , as cultural taboos often deter exploitation more reliably than enforcement alone in rural areas. In forestry contexts, sustainable management focuses on regulated harvesting in production forests, guided by guidelines for species-specific plans that account for slow growth rates and regeneration challenges; Central African initiatives recommend monitoring recruitment and implementing reduced-impact logging to minimize canopy damage and promote natural regeneration. Agroforestry systems offer viable alternatives, with M. excelsa showing compatibility in multi-species plantings that enhance soil fertility and provide economic incentives through timber and non-timber products, as demonstrated in trials supporting its integration into smallholder landscapes. Reforestation projects, such as the Restoration Project in , target degraded areas by planting over 18,000 hectares, incorporating site-specific techniques to boost seedling survival against pests like Phytolyma lata and improve potential. In agricultural matrices, like southern Benin's Dogbo district, strategies include designating protected trees within farmlands and promoting enrichment planting to counter from . Overall, combining community-based protections with scientific monitoring addresses primary threats of and loss, aligning with IUCN's near-threatened status to prevent further decline.

Cultural and historical context

Traditional significance

In West African cultures, particularly among the Yoruba and peoples of , Milicia excelsa (commonly known as ) is revered for its spiritual and mystical attributes, often regarded as a dwelling place for ancestral spirits, deities, or . Among the Yoruba, the tree is associated with the , symbolizing strength, longevity, and spiritual power, with rituals involving offerings or sacrifices performed beneath its canopy to seek protection or favor from these entities. In traditions, trees are linked to beliefs and divine origins, viewed as planted by (the supreme god) to nurture souls, with their deep roots anchoring sacred sites and inspiring taboos against arbitrary felling without proper rites. The tree's foliage and presence feature prominently in practices and across regions like and , where it serves as a conduit for communicating with ancestors or invoking blessings, reflecting broader animistic views of trees as living embodiments of forces. Gifts, libations, or ceremonial products derived from are offered during rituals near homes, palaces, or groves, underscoring its role in maintaining cultural harmony with the realm and enforcing taboos on . This significance contributes to informal strategies, as harvesting is often restricted by sanctions rather than formal laws.

Historical exploitation

Milicia excelsa, known commercially as , faced intensive selective during the colonial era in tropical , as European powers extracted high-value timber for , railway sleepers, and due to its durability and resistance to decay. In colonies such as , iroko was utilized for creosoted sleepers expected to last 30 years, exemplifying systematic exploitation under scientific forestry policies that prioritized export over regeneration. In Nigeria's Province, foreign firms—primarily —held over 90% of timber concessions, fueling a colonial timber boom that by 1960 contributed £7 million in exports, with iroko among the prized hardwoods targeted amid broader forest depletion. This historical overharvesting, spanning past centuries particularly in , reduced population densities and haplotypic diversity, as mature trees were felled without adequate replacement, contrasting with less impacted Central African stands. Early 20th-century practices often ignored sustainable yields, exacerbating vulnerability in sacred or riparian habitats where held cultural significance, setting precedents for ongoing threats from unregulated commercial demand.

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