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Madhuca diplostemon
Madhuca diplostemon
Madhuca diplostemon
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8°49′02″N 76°40′48″E / 8.81731°N 76.67998°E / 8.81731; 76.67998

Madhuca diplostemon
Scientific classification Edit this classification
Kingdom: Plantae
Clade: Tracheophytes
Clade: Angiosperms
Clade: Eudicots
Clade: Asterids
Order: Ericales
Family: Sapotaceae
Genus: Madhuca
Species:
M. diplostemon
Binomial name
Madhuca diplostemon
(C.B.Clarke) P.Royen

Madhuca diplostemon is a species of flowering plant in the family Sapotaceae, endemic to India.[1] It is a threatened tree species of the Western Ghats whose original specimens were collected in 1835, and it was considered extinct for 184 years until a single living specimen was discovered in a sacred grove in Kollam district, when scientists at the Jawaharlal Nehru Tropical Botanic Garden and Research Institute (JNTBGRI) identified the tree as Madhuca diplostemon rather than the common attilippa (Madhuca neriifolia).[2]

Leaf

The lone mature tree is located at the Koonayil Ayiravilli Shiva temple at Paravur, Kollam, Kerala. Surveys in other sacred groves in Kollam district failed to find another tree of the species. Since the species is represented by only one specimen in a single locality, it is eligible to be categorized as 'Critically Endangered' by the IUCN (International Union for Conservation of Nature), the JNTBGRI has noted.[3]

References

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Madhuca diplostemon

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from Grokipedia
Madhuca diplostemon (C.B. Clarke) P. Royen is a critically endangered in the family , endemic to the southern of , . This small , reaching up to 4 meters in height with fissured yellowish-white bark, features obovate coriaceous leaves measuring 3–14 cm long and 1.5–8 cm wide, dark green above and pale beneath. It produces pedicellate flowers in fascicles of 3–8, with four ovate sepals 8–10 mm long, and ellipsoid berries 2–3 cm long, flowering and fruiting from to . Native to seasonally dry tropical biomes at low elevations around 40 meters, the was first collected in 1835 by Robert Wight and formally described in 1848, but was presumed extinct for 184 years until its rediscovery in 2020 within the sacred Ayiravilli Grove near Paravur in . As of 2023, M. diplostemon was represented by a single mature individual and fewer than 30 young saplings (2–10 years old) in this protected grove; by 2024, conservation efforts had raised nearly 50 established seedlings. The species faces severe threats including habitat modification from construction, heat-induced flower drop, low fruit set, and predation by fruit bats and birds. Conservation initiatives, led by the Jawaharlal Nehru Tropical Botanic Garden and Research Institute in collaboration with the Kerala Forest Department since 2022, have achieved 70–80% seed germination success and resulted in the planting of the first propagated seedling in 2023; further efforts in 2024–2025 included successful vegetative propagation trials and additional sapling plantings for ex-situ conservation. These efforts underscore the species' precarious status and the importance of sacred groves in preserving biodiversity hotspots amid ongoing anthropogenic pressures in the Western Ghats.

Taxonomy

Classification

Madhuca diplostemon belongs to the kingdom Plantae, phylum Tracheophyta, class Magnoliopsida, subclass Asteridae, order Ericales, family Sapotaceae, genus Madhuca, and species M. diplostemon. The species was originally described as Isonandra diplostemon by C.B. Clarke in the Flora of British India in 1882, based on specimens collected in the Western Ghats, and later transferred to the genus Madhuca by P. van Royen in 1960, with the accepted binomial authority (C.B. Clarke) P. Royen. Within the family, which comprises approximately 800 species of mostly tropical evergreen trees and shrubs characterized by the production of milky , simple alternate leaves with entire margins, and cauliflorous inflorescences, the Madhuca includes about 100 species of trees native to and the Pacific, often valued for their timber, fruits, and latex-yielding properties.

Nomenclature and etymology

Madhuca diplostemon was first described as Isonandra diplostemon by Charles Baron Clarke in the third volume of Flora of British India in 1882, based on specimens from the southern . In 1960, Pieter van Royen transferred the species to the genus Madhuca in a revision published in Blumea, establishing the currently accepted name Madhuca diplostemon (C.B. Clarke) P. Royen. The synonym Isonandra diplostemon C.B. Clarke reflects its initial placement in the genus Isonandra, which was later subsumed under Madhuca as part of broader taxonomic rearrangements in the family. The genus name Madhuca originates from the Sanskrit term "madhuca," derived from "madhu" meaning , in reference to the nectar-producing flowers of species in this genus that are valued for their role in honey production. The specific "diplostemon" comes from the Greek roots "diplo-" (double) and "stemon" (), denoting the floral characteristic of having stamens in two series. The type material consists of specimens collected by the Scottish surgeon-botanist Robert Wight in December 1835 from Quilon (present-day , , ), during his botanical explorations in the region. A lectotype was later designated as Wight 583, housed at the of the Royal Botanic Gardens, (K000777740).

Description

Morphology

Madhuca diplostemon is a small reaching up to 4 meters in height, characterized by fissured bark with a yellowish-white blaze and thick, sticky, white . The branchlets are angular, measuring 2–6 mm in diameter and glabrous, while terminal buds are 2.5–3.5 mm long and sparsely covered with ferruginous hairs. Stipules are minute, lanceolate, approximately 1 × 0.5 mm, and caducous. The leaves are spirally arranged and crowded toward the branch tips, exhibiting an obovate to narrowly obovate shape, with dimensions of 3–14 × 1.5–8 cm. They are coriaceous, glabrous, dark green on the upper surface, and pale on the lower surface, with petioles 7–14 mm long. Reproductive structures include axillary fascicles of 3–8 flowers, with pedicels 1–1.5 cm long that are ferruginous tomentose when young. The flowers feature four ovate sepals, each 8–10 × 6–8 mm, and a campanulate corolla that is 7–8-lobed and 1.5–1.8 cm long, glabrous with oblong-obovate lobes rounded at the apex. The androecium is diplostemonous, with 15–19 stamens arranged in two whorls; filaments are subulate, and the style is slender, measuring 2–2.5 cm long. The is superior, oblongoid, approximately 0.5 cm long, glabrous, and contains 6–8 locules, each with one . Fruits are berries, 2–3 × 0.8–1 cm, beaked and glabrous. Each fruit contains a single , which is narrowly , laterally compressed, 2–2.5 × 0.6–0.8 cm, pale brown, slightly rugulate, and shining. These seeds are recalcitrant, exhibiting 70–80% success, often enhanced by hot water treatment. Distinguishing traits from related species such as Madhuca insignis include glabrous young shoots, minute lanceolate stipules, obovate leaf lamina, densely tomentose young pedicels, and an oblongoid ovary. In contrast to the closely related Madhuca balakrishnanii, M. diplostemon has shorter stipules, more densely hairy pedicels, and inner sepals that are less hairy abaxially.

Phenology and reproduction

Madhuca diplostemon exhibits a distinct , with flowering and fruiting occurring synchronously from January to March. Flowers are borne in axillary fascicles of 3–8 pedicellate blooms, featuring four sepals and a 7–8-lobed campanulate corolla, which supports rapid fruit maturation shortly following . The fruits are berries measuring 2–3 × 0.8–1 cm, glabrous and beaked, each containing a single narrowly approximately 2–2.5 × 0.6–0.8 cm in size. Pollination in Madhuca diplostemon is presumed to be entomophilous, consistent with the general reproductive strategy observed across the family, where insect vectors such as bees and flies predominate; however, this remains unconfirmed due to the species' extreme rarity and the solitary known individual. production is characterized by , as evidenced by the emergence of twin seedlings from individual seeds during experimental propagation efforts in 2023, suggesting potential for both sexual and clonal reproduction. trials using seeds from fallen fruits have achieved success rates of 70% in untreated controls and up to 80% with hot-water pretreatment, confirming seed viability despite their recalcitrant nature. Vegetative propagation trials, including stem cuttings treated with gel (100% rooting success) and air layering (rooting in 100 days), have shown promise for as of 2025. Reproductive challenges are pronounced in the known population, which comprises a single mature tree, with limited natural regeneration, including fewer than 30 young saplings (aged 2–10 years as of 2023) observed in the grove. This scarcity of viable offspring, potentially attributable to the tree's isolation, underscores the species' vulnerability and the critical need for assisted propagation to sustain the population.

Distribution and habitat

Geographic range

Madhuca diplostemon is an endemic tree species restricted to the southern Western Ghats in the state of Kerala, India. Its distribution is confined to this biodiversity hotspot, with no records from adjacent regions or other parts of the Western Ghats. Historically, the species was first collected in 1835 from the Travancore region, now part of southern Kerala, by botanist Robert Wight. At that time, imprecise locality data on type specimens led to presumptions of a wider distribution across low-elevation forests of the Deccan Peninsula prior to 1900, though subsequent surveys failed to confirm occurrences beyond Kerala. As of 2023, only a single mature individual is known, located at the Koonayil Ayiravalli temple in district, at an elevation of 40 m. Extensive surveys of over 1,100 sacred groves, primarily in , and other potential habitats in southern and the have not located additional populations. The extent of occurrence is estimated at less than 100 km², limited to this single site, which qualifies the species as Critically Endangered under IUCN criteria.

Habitat characteristics

Madhuca diplostemon inhabits lowland sacred groves in the of southern , , at elevations of approximately 40 m. These microhabitats consist of protected forest remnants that shield the species from logging and agricultural expansion, preserving undisturbed patches amid surrounding human-modified landscapes. The single known mature individual grows in front of a temple in the Ayiravalli near district, where the surrounding area is paved, limiting immediate associated vegetation. https://rheedea.in/storages/submission/file/33009983.pdf The species occurs in a tropical monsoon biome characterized by semi-evergreen to moist deciduous forests, typical of low-elevation Western Ghats foothills. The type locality suggests a historical habitat of seasonally dry tropical forests, potentially associated with regional dipterocarps, but the current site is highly modified with no vegetation associates. Preferred soils are well-drained lateritic types common in the region, supporting tree growth in undulating terrain. Annual rainfall averages 2,400–2,700 mm, predominantly during the southwest monsoon from June to September, with a pronounced dry season from December to May that influences seasonal growth patterns. Mean temperatures range from 22.4°C to 36°C, creating warm, humid conditions year-round. https://forest.kerala.gov.in/wp-content/uploads/2025/02/rettree.pdf https://kollam.nic.in/en/about-district/ https://cgwb.gov.in/old_website/District_Profile/Kerala/kollam.pdf https://dmg.kerala.gov.in/wp-content/uploads/2020/01/dsr_kol.pdf

Conservation

Status and threats

Madhuca diplostemon is assessed as Critically Endangered under IUCN criteria B2ab(iii) and D. This classification stems from its severely restricted area of occupancy, estimated at less than 10 km² within a single known location in the Ayiravilli Sacred Grove, , , coupled with a continuing decline in quality due to anthropogenic pressures. The species meets criterion B2ab(iii) because of the limited extent of occurrence and observed degradation in its , while criterion D applies given the extremely small population size. The wild population comprises a single mature , estimated to be over a century old, with no evidence of successful reproduction for approximately 184 years prior to recent observations; this results in an approaching zero. Although around 30 saplings (aged 1–10 years) have been documented in the vicinity, no juveniles or additional mature individuals exist in the wild, underscoring the species' precarious status despite the 2020 rediscovery. Major threats include habitat loss and fragmentation from , , and illicit in the . Local development activities, such as temple expansions and concrete paving around the sole mature tree, have directly degraded the site and likely contributed to the historical decline by removing potential individuals. exacerbates these issues through heat stress, causing premature flower and reduced fruit set, while predation by fruit bats (Pteropus giganteus) and birds further limits regeneration; age-related decline in the mature tree's vigor compounds the risk of .

Rediscovery

Madhuca diplostemon was first collected by the Scottish surgeon-botanist Robert Wight in December 1835 near Kollam (formerly Quilon) in Kerala, India. Wight initially described the species as Diospyros obovata in his 1848 publication Icones Plantarum Indiae Orientalis, volume 4, plate 1226. Later, in 1882, Charles Baron Clarke transferred it to the genus Madhuca as Bassia diplostemon (now synonymous with Madhuca diplostemon) in The Flora of British India, volume 3. These early descriptions were based on herbarium specimens, with no live plants documented beyond the initial collections. Following its initial discovery, Madhuca diplostemon entered a prolonged period of absence, with no verified sightings or collections recorded from approximately 1836 until 2019—a hiatus spanning 184 years. The was absent from extensive botanical surveys of endemics, including those documented in Nayar and Sastry's 1990 Red Data Book of Indian Plants and subsequent explorations by Rakesh (1993) and Oldfield et al. (1998). It was presumed extinct due to the lack of field evidence and the ongoing threats to lowland evergreen forests in southern . The species was rediscovered on 22 January 2019 by a team from the Tropical Botanic Garden and Research Institute (JNTBGRI) in Palode, , led by researchers Shailajakumari S., Santhosh Kumar E.S., Sreekala A.K., Parthipan B., and R. Prakashkumar. The single mature individual, approximately 4 meters tall, was located in the Koonayil near Paravur in , , a protected temple area that has preserved native vegetation. Confirmation came through detailed morphological examination, matching the plant's features—such as its fissured bark, spirally arranged leaves, and flower structure—to the type specimens housed at the herbaria of (K000777740) and (E00179201, E00277959). This marked the first live encounter with the species in nearly two centuries. The rediscovery held significant implications for conservation, as it provided the first evidence of a surviving and prompted a reassessment of the species' status under IUCN criteria, elevating it to Critically Endangered due to the presence of only one known mature individual. The event underscored the ecological value of sacred groves in preserving amid habitat loss. Details of the find were formally documented in a article in the journal Rheedea (volume 30, issue 2, pages 270–277), highlighting its rarity as an endemic to the southern .

Conservation efforts

Ex-situ conservation efforts for Madhuca diplostemon have been led by the Tropical Botanic Garden and Research Institute (JNTBGRI) through its species recovery program, initiated following the species' rediscovery in 2020. In late 2020, JNTBGRI collected seeds from fallen fruits around the sole known mature tree at the Ayiravilli , marking the first ex-situ collections for the species, as none existed prior. By 2022–2024, these efforts expanded to include nursery-raised for trials, with a dedicated propagation house (10 x 7.5 m) equipped with automated mist irrigation established in 2023 to support seedling growth. Additionally, 82 seedlings were successfully raised from 135 collected seeds during the first year of a dedicated project (January–December 2023). Propagation methods have focused on both seed-based and vegetative approaches to enable mass multiplication. Conventional vegetative propagation via stem cuttings achieved 70% rooting success in controls and 100% when treated with gel, evaluated after 70 days in June 2023 trials; air layering and approach both yielded 100% success, while grafting reached 60% survival on Madhuca neriifolia rootstocks. propagation has benefited from , with twin seedlings produced from polyembryonic seeds observed and reported for the first time in 2023, aiding in rapid seedling production during germination studies that showed 70% success overall (80% with hot water pretreatment). via was also initiated in 2023 due to limited seed viability, complementing these efforts. In-situ measures emphasize protection of the single known population at the Ayiravilli Sacred Grove in Kollam district, Kerala, where the mature tree and approximately 30–50 surrounding saplings (2–10 years old) are safeguarded through community reverence and legal protections under Kerala forest laws, including the Kerala Forest (Vesting and Management of Ecologically Fragile Lands) Act. Community awareness programs have been integrated into conservation activities to mitigate threats like habitat alteration from nearby construction, with ecological and edaphic data collected during multiple exploration trips to monitor the site. A notable achievement was the planting of a propagated sapling by the Kerala Chief Minister on June 5, 2023, at a government school in Thiruvananthapuram to promote public engagement. Future plans include reintroduction trials in botanic gardens and suitable habitats within the , alongside potential habitat restoration to expand the population beyond the sacred grove. Genetic studies are planned to assess diversity, which is currently absent due to propagation relying on a single clone from the known tree, limiting variability. These initiatives are part of a three-year eco-restoration project (2023–2025) with a of Rs 15,04,200. Collaborations involve JNTBGRI partnering with the Kerala Forest Department, with funding from the Indian government via the department's allocation (first installment Rs 6,01,680 in 2023). The species' Critically Endangered status on the has informed these efforts, though direct IUCN implementation support is not specified.

References

  1. https://powo.science.kew.org/taxon/urn:lsid:ipni.org:names:787467-1
  2. https://www.cambridge.org/core/journals/oryx/article/conservation-of-madhuca-diplostemon-a-critically-endangered-tree-endemic-to-the-western-ghats-india/6CEAA3752EFBF6FDBBE086F8CEE855D2
  3. https://dx.doi.org/10.22244/rheedea.2020.30.03.03
  4. https://www.researchgate.net/publication/383532715_First_Year_Report_%27Conservation_Eco-restoration_and_Popularisation_of_three_endemic_and_threatened_tree_species_of_Kerala
  5. https://www.ijfmr.com/papers/2025/4/54624.pdf
  6. https://keralabiodiversity.org/wp-content/uploads/2025/02/Annual-report-2023-2024_English.pdf
  7. https://rheedea.in/storages/submission/file/33009983.pdf
  8. https://powo.science.kew.org/taxon/urn:lsid:ipni.org:names:30000114-2/general-information
  9. https://powo.science.kew.org/taxon/urn:lsid:ipni.org:names:36784-1
  10. https://www.researchgate.net/publication/352877236_Madhuca_balakrishnanii_Sapotaceae_a_new_species_from_Kerala_India
  11. https://www.biologydiscussion.com/angiosperm/dicotyledons/sapotaceae-characters-distribution-and-economic-importance/48215
  12. https://doi.org/10.54207/bsmps2000-2023-Y6XIRU
  13. https://dx.doi.org/10.22244/rheedea.2020.30.02.02
  14. https://www.thehindu.com/news/national/kerala/extinct-tree-found-after-180-years-in-kollam-grove/article32760018.ece
  15. https://www.researchgate.net/publication/372684390_Madhuca_diplostemon_-a_vanishing_imperilled_endemic_tree_of_the_Western_Ghats
  16. https://www.cornous.com/downloadpdf/279
  17. https://forest.kerala.gov.in/forestapp/public/documents/publications/file0311202512:25:35.pdf
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