A digital multi-access key for easy identification of large tree species of ebony wood in Madagascar

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The paper develops an interactive digital multi-access identification key for Madagascar’s large ebony-producing trees in the genus Diospyros, motivated by CITES-listed overexploitation and gaps in species identification along the value chain. Using the Lucid application, the authors build a user-friendly tool based on 109 informative morphological and eco-geographic characters—prioritizing vegetative traits (e.g., bark, stems, leaves) that can be assessed even without flowers or fruits—supplemented with photos, illustrations, and a glossary covering 88 Diospyros species meeting size thresholds (≥20 cm DBH and/or ≥20 m height). The key is presented as the first Lucid-based identification key designed for Madagascar species, with the key caveat implicit in its focus on certain tree size classes and on characters intended for field use rather than reproductive structures. This paper does not explicitly discuss endometriosis or adenomyosis; it was included in the corpus via a keyword match in the upstream search index.

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Abstract

In 2013, all populations of the precious wood g enera Dalbergia (Fabaceae) and Diospyros (Ebenaceae) from Madagascar were placed on CITES Appendix II in an effort to combat unsustainable and illicit over -exploitation and illegal exportation for the international market. The accompanying Action Plan adopted by CITES identified several information and cap acity gaps, which undermine the sustainable and equitable management of these valuable resources. These gaps include the lack of practical, reliable tools to identify species along the entire value chain, from standing trees to cut wood and finished products. To address this need, we developed simple, user-friendly, multi-access keys for the two genera in Madagascar using the Lucid application. This new tool provides highly accurate identification of standing and felled trees to assist actors in the forestry, regulatory, and natural resource management sectors, including customs officials and law enforcement authorities as well as conservationists and protected area managers. In this paper, we focus on the development of the Diospyros identification tool. Th is interactive, electronic key employs 109 informative characters, including morphological features, emphasizing vegetative structures such as bark, stems, and leaves that are present even in the absence of flowers and fruits, in conjunction with eco -geographic characters (bioclimate, elevation, and geography). The key is supplemented with photos, illustrations, and a comprehensive glossary, to deliver accurate identification of the 88 Diospyros species that are large enough to be potential sources of comme rcially valuable ebony wood (≥ 20 cm DBH and/or ≥ 20 m height). This is the first use of Lucid to develop an identification key for species in Madagascar, paving the way for its application to other taxa for which practical electronic field identification is needed. Key words: CITES, Diospyros, ebony, Lucid 4, Madagascar, multi-access key, precious woods. Author-formatted, not peer-reviewed document posted on 16/08/2024. DOI:  https://doi.org/10.3897/arphapreprints.e134616 2

Introduction

Over the last two decades’ members of the precious wood genera Diospyros (Ebenaceae) and Dalbergia (Fabaceae) have faced rapidly growing pressure and worsening threats due to unsustainable levels of illicit exploitation, primarily within legally protected areas. Most of the ebony and rosewood timber obtained from them has been harvested illegally and exported fo r the international market, primarily to China (Global Witness & Environmental Investigation Agency 2009, 2010; Schuurman and Lowry 2009; Wilmé et al. 2009; Randriamalala and Liu 2010; Randriamalala et al. 2011; Ballet et al. 2011; Waeber et al. 2015; Andriamanana 2019). As part of Madagascar’s obligations under the Convention on Biological Diversity (CBD) signed in Rio de Janeiro in 1992 (Stone 1996) and the Convention on International Trade of Endangered Species (CITES 1978), the government is responsibl e for ensuring the sustainable management and protection of all its species and for guaranteeing that their utilization does not threaten their survival. Measures to achieve a permanent halt to illegal exploitation in order to establish policies for rational and sustainable management of precious woods as well as for the equitable sale of these valuable resources have recently been initiated (Innes 2010 ; Pepke et al. 2015) . Furthermore, in 2013, all Malagasy species of both Diospyros (which produces ebony wood) and Dalbergia (the primary source of rosewood) were listed on CITES Appendix II in an attempt to reduce over -exploitation and commercial trafficking (Andriambololonera et al. 2013; CITES 2013a, b). That same year, at the 16 th CITES Conference of Parties, an Action Plan was adopted (Decision 16.152 and subsequently Decision 17.203) requiring the establishment of an embargo on the export of wood stockpiles that had accumulated following seizure by the Malagasy authorities and prohibiting commercial excha nge of ebony and rosewood (Andriamanana 2019). Yet despite these efforts, exploitation has continued (Ballet et al. 2011; Mason et al. 2016; Ratsimbazafy et al. 2016). Moreover, significant gaps were identified regarding the scientific knowledge base of th ese precious wood genera, which prompted a series of recommendations in the Action Plan to address them (CITES 2018). One of the most important issues identified in the Action Plan was the inability to provide correct scientific names and reliable identifi cations for species, which are the principal unit of CITES management and a key element of biodiversity. This situation is due in large part to the lack of efficient identification tools (Delaunay 2020). Moreover, actors involved in the Malagasy forestry s ector use generalized designations for various types of precious wood, either in the form of common (vernacular) names (which vary regionally) or commercial names based on the color and other characteristics of the wood being exploited. However, these names often apply to two or more distinct species, and they are used inconsistently. For example, all species of Diospyros with black heartwood are called ‘ebony’ or ‘hazomainty’ in Malagasy, and species of Dalbergia with red or deep pink-violet heartwood are called ‘rosewood’, or ‘andramena’. Consequently, commercial and scientific names represent fundamentally different concepts in the context of the sustainable management of these important resources and the species from which they are sourced (Rakotovao et al. 2012). Addressing the challenges associated with the accurate identification and naming of species is a major hurdle for the eventual relaxing or lifting of the current embargo on these two genera by means of establishing a non-detriment finding (NDF) for a species whose exploitation would be possible without compromising its survival (Mason et al. 2016) or by removing them for CITES Appendix II . Therefore, it is crucial to develop methods and tools that allow for the accurate, precise, and unambiguous identification of species. This is particularly important when evaluating and managing populations of precious wood species, as it informs decision -making regarding their conservation, management, and exploitation. Author-formatted, not peer-reviewed document posted on 16/08/2024. DOI:  https://doi.org/10.3897/arphapreprints.e134616 3 To help address the objective s of the CITES Action Plan for Madagascar , a consortium was established in 2017 to develop scientific knowledge and tools in support of the sustainable management of the country’s precious wood genera Dalbergia and Diospyros (the consortium is known by its French acronym G3D – Gestion Durable des bois précieux Dalbergia et Diospyros de Madagascar). The management and control of these species requires reliable identification along the entire value chain, from standing trees and cut logs in the forest to sawn wood and finished products, and each of these stages requires its own methods and tools. A multi -disciplinary approach was therefore adopted that comprises four complementary components: • Taxonomy (documentation of populations, field collection of represe ntative samples, and clarification of species delimitation). • Development of practical, reliable identification tools for standing trees and for specimens with leaves, flowers and/or fruits. • Establishment of forensic identification methods based on the stud y of a) comparative wood anatomy, b) DNA sequencing (barcoding), and c) near infrared spectroscopy. • Development of effective management strategies for the conservation of wild populations. Collectively the main objective of these components is to establish a solid scientific base of research

Material

and associated knowledge to inform accurate delimitation and identification of potentially exploitable species of Diospyros and Dalbergia for their effective management and for forensics. As part of this initiative, work was undertaken to develop practical identification tools for both genera based on morphological and eco -geographic characters, as part of the G3D taxonomy component led by the Missouri Botanical Garden’s Madagascar Program. Identification keys are generally based on morphological characters of plant organs and are primarily used to distinguish species based, as far as possible, on easily observed features. Keys primarily make use of the inflorescence structure and of characteristics of the flowe rs and fruits, often complemented by characters of the leaves as well as other aspects such as the plant’s growth form or habit. They are nearly always dichotomous and are generally structured for publication in scientific articles or in floras and guidebooks. In this type of key, the sequence in which information is presented to the user is pre-determined by the author, usually by offering the user two mutually exclusive choices (a “couplet”) at each step by means of a text description of one or more alternative diagnostic characters (Judd et al. 1999; Hagedorn et al. 2010; Griffing 2011), leading either to another couplet or to an identification. However, when attempting to make an identification in the field, and especially if confronted with a sterile individual (lacking flowers and fruits, which is often the case when conducting forest inventories), dichotomous keys based primarily or exclusively on reproductive organs are difficult if not impossible to use. Even when flowers and/or fruits are available, a key that employs specialized terminology can present problems that render it impractical to users not familiar with technical jargon. Moreover, published dichotomous keys cannot easily be modified or updated if new information becomes available or new, morphologically similar species are recognized (Hardisty & Roberts 2013; Mangold 2013; Zuquim et al. 2017). One way to overcome these constraints is to develop keys that combine traditionally used characters with new, informative featu res that have been underutilized or ignored, such as those involving vegetative structures, which are more likely to be observable regardless of the phenological stage, even in the absence of flowers and fruits. Leaf features are particularly pertinent in that they often enable recognizing and distinguishing among closely related taxa (Hickey et al. 1999, Ellis et al. 2009) . Similarly, while the utility of bark features for recognizing tree species is well known in temperate areas Author-formatted, not peer-reviewed document posted on 16/08/2024. DOI:  https://doi.org/10.3897/arphapreprints.e134616 4 for genera such as Acer, B etula, Picea , Populus, and Quercus, among others (Biswas et al. 2016; Carpentier et al. 2018; Wu et al. 2021; Juola et al. 2022), bark characters have not been used widely in tropical regions and very little in Madagascar. While bark characters have not be en utilized previously for species delimitation and recognition of Malagasy Diospyros, field observations have clearly revealed significant variation among species, suggesting that they are of potential use for field identification. Similarly, eco-geographic characters such as bioclimate, vegetation type, and elevation, which have proven to exhibit species-specific patterns and to be highly informative for species delimitation (Lowry et al. 1999; Vences et al. 2009; Rabarimanarivo et al. 2015; Crameri et al . 2022), are also of potential value for informing accurate identification. In the age of global access to information via the internet and the rapid development of bioinformatics tools and technologies, it is now possible to build interactive and richly illustrated, multi- access identification keys that are simple, practical, and efficient. Moreover, these keys can be accessed through portable platforms that function independently, without needing an internet connection. This is precisely the type of tool that is required to enable reliable identification of Malagasy Diospyros and Dalbergia, employing a data matrix (or character/species) multi-access type of key, a model that is now being widely used (Begum et al. 2012; Wati et al. 2021) . Early multi-access keys were based on the punch card approach (Hansen & Rahn 1969), in which an array of characters with two or more states that are not necessarily mutually exclusive are presented to the user, who is not required to follow a pre- determined sequence of steps (in contrast to conventional keys), but which can instead be used to select features in the order that best corresponds to the material being identified. This type of key is particularly advantageous when dealing with incomplete material (Ju dd et al. 1999, 2002). Several computer programs have recently been developed to produce interactive, matrix-based, multi-access identification keys (Dallwitz 2007; Gaubert et al. 2008; Hagedorn et al. 2010) such as DELTA and INTKEY (Dallwitz 1993), FRIDA (Martellos 2010), LINNAEUS (Wati et al. 2018), Lucid (Norton et al. 2000), and Xper versions 2 et 3 (Ung et al. 2010; Vignes -Lebbe et al. 2016; Lombard et al. 2021). They all exploit practical and flexible methods for coding characters, and some can incorp orate illustrations (photos, drawings, and maps), as well as videos, links to internet sites, and a glossary. The major advantages of these keys are that they facilitate identification even when material is incomplete and are accessible for a wide range of users, including those less familiar with the organisms being identified than professional taxonomists. One of the main objectives of the taxonomic component of the G3D project is to produce a tool that can be used at the beginning of the precious wood va lue chain to obtain a reliable species identification for each potentially exploitable tree of Diospyros and Dalbergia, a required step for the sustainable management of these resources. To meet this need, the identification tool must work reliably for trees that are still standing or that were recently felled, even if flowers or fruits are absent. After a careful comparison of the advantages and drawbacks of each of the applications mentioned above, Lucid was considered to be the best adapted to meet Madag ascar’s current needs for accurate field identification. Lucid has already proven to be effective for the development of practical identification keys for a wide diversity of objects, ranging from minerals to fossil bacteria and living animals, such as certain insect groups, as well as algae and vascular plants (many examples in these and other groups can be found on the Lucid website: http://lucidcentral.org/). The work presented in this paper summarizes the development of a practical key using Lucid 4 to facilitate the accurate and reliable identification of Malagasy species of Diospyros that are potential sources of commercially valuable ebony wood. As for large tree species of Dalbergia (Phillipson et al. Author-formatted, not peer-reviewed document posted on 16/08/2024. DOI:  https://doi.org/10.3897/arphapreprints.e134616 5 2023), a separate key has been developed using the same software and following the same principles and methods but is not discussed further in this paper. Diospyros comprises an estimated 903 species of which 763 have been described to date, distributed across the main tropical regions (see the following for examples of recent taxonomic accounts of Diospyros spp. from various parts of the world: Tang et al. 2019; Schatz et al. 2021b; Puglisi et al. 2022; Hassler 2023; POWO 2023) and the remainder are currently in the process of being formally described. Madagascar represents one of the main centers of diversity for the genus, as indicated by the first comprehensive revision for the island publi shed by Perrier de la Bâthie (1952a, b), who recognized a total of 97 species. However, collections and field observations made over the following decades clearly revealed the presence of far greater species diversity, and this catalyzed a new effort to do cument and describe Malagasy Diospyros starting some 15 years ago. This has led to the recognition of an estimated 285 species on the island, 145 of which have now been described and all but two of which are endemic to Madagascar (Schatz and Lowry 2018; Sc hatz and Lowry 2020; Schatz et al. 2020, 2021a, 2021b; Linan et al. 2021; Mestre et al. in press; Rakouth et al. 2023), while an additional ca. 140 endemic species remain to be described (Madagascar Catalogue 2024). Field work conducted as part of the G3D project has contributed significantly to the available collection base, whose taxonomic component has now clarified the delimitation and completed the description of all 88 ‘large tree’ species (Lowry et al. 2024), each of which is regarded as a potential source of commercially valuable ebony wood by virtue of the fact that it has been documented to reach a diameter at breast height (DBH) of ≥ 20 cm and/or a height of ≥ 20 m (Schatz et al. 2021b). Species of Diospyros are found throughout all regions of Mad agascar, but depending on a given species’ ecological preferences (altitude, substrate, habitat, etc.), they will generally be found in just one or two of Madagascar’s principal native vegetation types, including evergreen humid forest in the east, woodland or shrubland in the west, and deciduous dry forest in the north (often on karstic limestone, known as ‘tsingy’) or the south, as well as spiny thickets in the south and southwest (species of Diospyros are rare in montane vegetation). Some have wide geographical ranges, occurring across large proportion of one or two of the island’s main bioclimatic regions, as defined by Cornet (1975) and simplified by Schatz (2000), while others have highly restricted ranges (Madagascar Catalogue 202 4). A species’ eco -geographic preferences comprise valuable information that can complement morphological characters for developing identification keys (Wati et al. 2018; Lombard et al. 2021). With this in mind, we tested the value of including eco-geography in building our identification tool for large tree Diospyros species using the Lucid platform. The tool we present here was designed primarily to assist an array of actors involved in various aspects of the management and control of Madagascar’s forestry sector, in particular with regard to inventories of standing trees. These stakeholders include forestry agents, operators involved in wood harvest (including both landowners and concession holders), managers of protected areas and other conservation sites, customs of ficials, and officers of the judiciary police, among others. Moreover, because the key we have developed enables users to identify dried collections (i.e., herbarium specimens) as well as living material, it will also be of value to researchers, field botanists, and students to improve their knowledge of the Malagasy species that are potential sources of commercially valuable ebony wood and strengthen their ability to recognize them.

Materials and methods

Lucid 4 software Author-formatted, not peer-reviewed document posted on 16/08/2024. DOI:  https://doi.org/10.3897/arphapreprints.e134616 6 For an identification tool to perform well and respond to Madagascar’s needs for managing precious woods by enabling accurate identification of standing trees and dried specimens, it must be simple, practical, interactive, and portable. Among the various programs available to produce i nteractive, electronic, matrix -based or multi -access keys, we selected Lucid version 4.0.4 (https://www.lucidcentral.org), which meets all of Madagascar’s needs for identifying large tree species of Diospyros in the field and herbarium. To our knowledge, Lucid keys have never been used before in Madagascar for species-level identification, even though keys can be distributed free of charge; only the developers are required to obtain a license to produce an operational tool. Utilization of a Lucid -based key does not require internet access, and it can easily be modified, corrected, and updated with little effort by the developer. However, the main reason we opted to employ this program is because it is simple to use and functions without an internet connectio n, making it particularly well suited for field identification in Madagascar, where there is usually no internet access. Moreover, Lucid keys can easily be shared and transferred (by e -mail, USB key, etc.) and can be used freely in any browser and on a wide range of platforms (laptops and tablets, or smartphones via a mobile application). Lucid is also practical and intuitive, allowing users to access a wide range of visual and text-based descriptors as well as species profiles (Vignes -Lebbe et al. 2016; Pi nel et al. 2017). The developer is provided with an efficient interface containing all the tools and functionality needed to organize and deliver supplementary information to the user (photos, line drawings, links to on-line sites, glossaries, etc.) for each species and for important of difficult-to-interpret characters, greatly increasing the user’s ability to grasp and understand terminology, thus improving their ability to obtain an accurate identification. To optimize the functionality and utility of th e Lucid-based tool we have developed, it was designed to perform well even in the absence of flowers and fruits and to remain robust and reliable even if the user misinterprets some characters. The tool thus provides efficient, multi -access entry according to the user’s needs and can deliver rapid and accurate identifications as well as valuable diagnostic information. Taxa Among the ca. 285 species of Diospyros recognized in Madagascar, 88 develop into large enough trees to be potentially exploitable for ebony wood (Lowry et al. 2024) and are therefore included in the Lucid key we have developed. Each species has its own particular geographic and bioclimatic distribution range, reflecting its ecological preferences. For example, within the island’s humid bioclimatic zone, D. squamosa is widely distributed in dense, humid, evergreen forests of the northwest and along the eastern escarpment (Schatz and Lowry 2020), whereas D. littoralis is restricted to littoral forests on sand near the eastern coastline (Schatz et al. 2021a). Other species have narrow ranges and are known from only a few sites, such as D. lowryi and D. ultima, both from low elevation humid forests in the northeast and known from only 2 and 4 localities, respectively (Schatz and Lowry 2018; Schatz et al. 2021a; Madagascar Catalogue, 202 4). Some species of Diospyros occur in dry, semi -deciduous forest on karstic limestone in the extreme north of the island, such as D. vescoi (which has a rather large range) and D. crassifolia (much more narrowly distributed) (Linan et al. 2021). Still other species occur in areas with similar vegetation in the west, such as D. tropophylla and D. sakalavarum, which have fairly large ranges, and D. subtrinervis, known from a single locality. The risk of extinction for each of the 88 large tree species was assessed between 2018 and 2021 according to the IUCN Red List criteria. A total of 45 species (51%) were a ssessed as threatened, including 5 that were found to be Critically Endangered (CR), 18 Endangered (EN), and 22 Vulnerable (VU), whereas 11 species were assessed as Near Threatened (NT), and 31 were regarded as Least Concern (LC). One species was Data Defi cient (DD) (IUCN Red List 2022). Author-formatted, not peer-reviewed document posted on 16/08/2024. DOI:  https://doi.org/10.3897/arphapreprints.e134616 7 Building the key The key was constructed in four steps, implemented in the application’s key -building interface (Lucid Builder), which comprises three tabs at the base of the tree panels [Tree View], [Spreadsheet Scoring] and [Score Analyser], as follows: 1) Data compilation within the [Tree View] tab 2) Data coding and entry within the [Spreadsheet Scoring] tab 3) Development of the key 4) Testing, feedback, and improvement The [Score Analyser] tab provides analyses of character differences and species polymorphism to assess and indicate where improvements can be made to the key. Data compilation within the [Tree View] tab Taxonomic entities backbone The first tab [Tree View] enables the developer to view the structure (sequence and hierarchy) of characters and character states in the ‘features’ panel as well as a list of the species in the ‘entities’ panel. The taxonomic entities backbone was establis hed by alphabetically entering the names of the 88 large tree Diospyros species in the [TreeView] tab. The species for which the key was developed are listed in Appendix 1 and can also be found on a dedicated page via the Catalogue of the Plants of Madagas car (Lowry et al., 2024). Features backbone The initial step of selecting characters and scoring character states involved preparing a list of potentially informative features of the stems, leaves, flowers, and fruits that vary among the large tree species of Malagasy Diospyros. Additional characters that could facilitate reliable field identification were then incorporated, in particular those that can only be observed in fresh material, including macroscopic features of vegetative organs such as the bark, which are easily observable throughout the year, even when an individual tree is sterile. For a key based exclusively on morphological data, the assumption is usually that any given species can occur anywhere within the geographic area being considered. This is clearly not the case, however, for Diospyros in Madagascar. We therefore compiled additional information on the ecological preferences of each species (bioclimate, altitudinal range, and vegetation type) as well as the potential geographic range for each species, to improve ease of identification by reducing the list of candidate species for a given site (Wati et al. 2018). The final selection of character features and the corresponding terminology included those that were determined to be the most pertinent for discriminating among the species and the easiest for users to interpret. The list of characters and states was entered into the ‘features’ panel on the [TreeView] tab of Lucid Builder. The features backbone of the key for the 88 species comprises data for morphological and eco - geographic characters, including a total of 109 characters and 356-character states (Table in Appendix 2). Compilation of data on morphological characters Data on morphological character states exhibited by each species were primarily collected from descriptions available in the literature, complemented and refined based on examination of specimens Author-formatted, not peer-reviewed document posted on 16/08/2024. DOI:  https://doi.org/10.3897/arphapreprints.e134616 8 available in the herbaria of the Parc Botanique et Zoologique de Tsimbazaza, Antananarivo, Madagascar (TAN), the Missouri Botanical Garden, St. Louis, Missouri, USA (MO), and the Muséum National d’Histoire Naturelle (MNHN), Paris, France (P), as well as scans of selected specimens available online. This was further enriched with field observations recorded by collec tors on specimen labels (Lombard 2021) and photos of living material, notably taken as part of the G3D project, showing details of habit, branching, bark, leafy branches, flowers, and fruits, which provide more precise information on character states seen on standing trees, whereas information obtained from the literature and pressed specimens is more informative for making identifications of herbarium material (Figure 1, Table in Appendix 2). As mentioned above, bark characters have been shown to be of val ue for species identification in temperate genera but have been less widely used in the tropical areas , including Madagascar, where scientists have only rarely used bark characters. In the absence of a standard method for describing bark features, we drew from the works of several authors (Letouzey 1969-1972; Junikka 1994; Rakotovao et al. 2012; Biswas et al. 2016; Carpentier et al. 2018 ) to identify those of potential value for Malagasy Diospyros. Three types of easy -to-observe characters were retained: bark surface texture (smooth, fissured, scaly, rugose), the presence of distinctive structures (lenticels, fissures, longitudinal and transverse striations, scales, a crust, crevasses, etc.), and overall color, both in vivo and in sicco (Figure 2). To compile information on these characters for each species, we examined photos of tree trunks and bark samples taken in the field, along with high resolution images of dried bark material associated with herbarium specimens (Figure 2). High resolution photos were taken at the Scientific Imaging Workshop (UAR 2700 2AD, BAOBAB facilities, DIM -MAP Île-de-France, CNRS and MNHN) located at the Muséum in Paris. For Madagascar, the use of bark features to identify species for the development of a practical identification tool represents pioneering work. Compilation of data on eco-geographical characters Information on ecological preferences and geographic distribution is also useful for facilitating the identification of Malagasy species of Diospyros given that each of them has its own distinctive specificities. We used QGIS (3.16.8 with GRASS 7.8.5) to visualize distribution data for each species (as a .kml points layer) and to record their eco-geographic characteristics using three key descriptors: • Madagascar’s five main bioclimatic regions (humid, subhumid, dry, subarid, and montane), based on the bioclimatic map of Cornet (1974) as simplified by Schatz (2000) • Five altitudinal classes between 0 and 2500 m (in 500 m increments); <500 m, <1000 m, <1500 m, <2000, and 2000 m or more. • Potential geographic distribution: actual and potential presence in Madagascar was recorded in cells of 1˚×1˚ resolution; potential presence was extrapolated from known occurrence points. Author-formatted, not peer-reviewed document posted on 16/08/2024. DOI:  https://doi.org/10.3897/arphapreprints.e134616 9 Figure 1. Photographs of selected large tree species of Diospyros, showing various morphological features of their leaves, fruit, and fruiting calyx. 1 D. aculeata, leaf apices terminating in a thorn and fruiting calyx completely enclosing the fruit (photograph by F. Ratovoson) 2 D. antsirananae , densely pubescent leaves and fruit, with reddish brown to ferruginous trichomes (photograph by S. Rakotonandrasana) 3 D. bernieriana, margins of the leaves undulate and fruiting calyx expanding to enclose the fruit completely and form a prominent collar (photograph by G.E. Schatz) 4 D. crassifolia, coriaceous, elliptic leaves and erect fruiting calyx lobes (photograph by S. Rakotonandrasana) 5 D. humbertiana, small, obovate leaves and fruiting calyx with 4 spreading lobes (photograph by P. Lowry) 6 D. labatiana, fruit surface and inner portion of calyx lobes covered by a white waxy substance (photograph by S. Andrianarivelo) 7 D. maculata, glabrous leaves and fruit with an entire (unlobed), cupuliform calyx (photograph by P. Lowry) 8 D. parifolia, subopposite to opposite, coriaceous, glabrous leaves (photograph by S. Andrianarivelo) 9 D. plicaticalyx, lenticellate, gray/grayish twigs and fruiting calyx with undulate and plicate margins (photograph by G.E. Schatz). Figure 2. Examples of the three bark characters utilized in the Lucid key for Malagasy Diospyros (texture, presence of distinctive structures, and color). A smooth, lenticellate, gray/grayish bark of D. ferrea. B smooth, fissured, gray/grayish to light brown bark of D. chitoniophora (left) and D. bardotiae (right). C rugose, light brown bark with longitudinal striations of D. brevipedicellata. D rugose, deeply fissured, cracked, dark brown to black/blackish bark of D. clusiifolia (left) and D. toxicaria (right) (all photographs by H.N. Rakouth). Author-formatted, not peer-reviewed document posted on 16/08/2024. DOI:  https://doi.org/10.3897/arphapreprints.e134616 10 Data scoring within the [Spreadsheet Scoring] tab Scoring of features and states that correspond to each species was done for both qualitative and quantitative characters using the second tab in the key-building interface [Spreadsheet Scoring], which contains the data matrix of characters and species . Those that can potentially be misinterpreted, e.g. certain leaf shapes (elliptic, oblong, ovate, etc.), can be recorded in Lucid in a way that accommodates for potential user error. By using this feature, species are retained in the final list of potential results that would otherwise have been excluded due to the incorrect selection a character state that is in fact not found in material belonging to the taxon. This is a helpful option since the interpretation of character states is not always straightforward and can vary between users. For a species that exhibits morphological variability, all possible character states are coded, enabling the user to select more than one state for a polymorphic feature. On the other hand, even if certain character states have not actually been observed on material of a given species, the person building the key can nevertheless select states that could reasonably be expected to be expressed and could therefore be encountered by a user or could be inadvertently selected due to a misinterpretation. To record information on the reliability of the states known for a particular character, a blue symbol is selected when the interpretation is verified and unambiguous, whereas a red symbol is chosen in situations where misinterpretatio n by the user is possible or likely. Rare or exceptional character states are indicated by a green symbol and those that are both rare and prone to misinterpretation are indicated in yellow. Finally, a question mark is used for characters whose state(s) is (are) uncertain or for which data are unavailable (Figure 3). The Lucid tool for Malagasy Diospyros has thus been designed to function regardless of which plant organs are available for identification and to be reliable even when there is a risk of potent ial errors for certain characters due to user misunderstanding or misinterpretation. Quantitative characters were counted or measured to code numerical values (#) in the data matrix table. This information was recorded in a table comprising four columns: o utside minimum value, normal minimum value, normal maximum value, and outside maximum value, in which the normal values are calculated as the most frequent class of observations [normal min - normal max] in all measured samples. For example, in Figure 3, the normal values are comprised in the class [0.8–0.9 cm] of the character “width of the largest leaf”, among 10 measured leaves. Counts or measurements were systematically made on an organ or structure regarded as being fully mature, and in order to standardize and facilitate comparison, the largest values were always used. For example, leaf dimensions were measured on the largest leaf on a leafy branch (Figure 3). To score the potential geographic distribution of each species treated in the key, a gr id comprising 75 cells, each with an area of 1˚×1˚, was superimposed over a map of Madagascar, which is situated between 11° to 25° S latitude and 43° to 50° E longitude. Taking into consideration the known range of each of the 88 Diospyros species as well as its eco -geographic preferences, the potential geographic range was scored in the appropriate cells. The convention used to name a given cell was based on the degree values for longitude and latitude corresponding to the points it encompasses. For examp le, the cell containing the coordinates of a population of D. aculeata located at 45°16’23” E longitude and 22°54’05” S latitude was labeled 4522, as shown in Figure 4 A-D. This allowed for scoring of longitudinal bands of presence, which, given the shape of Madagascar, were comparatively fewer in number than the alternative, using latitudinal bands of presence. Hence, the potential distribution of each species was characterized as a range within one or more longitudinal bands, and these were entered into Lucid as a quantitative variable with multiple independent ranges. We intentionally used a conservative approach for the process of estimating potential range, including all grid cells in which the species could reasonably be anticipated to occur. The resulting potential distribution was then systematically reviewed Author-formatted, not peer-reviewed document posted on 16/08/2024. DOI:  https://doi.org/10.3897/arphapreprints.e134616 11 and validated by comparison with expert information provided by field botanists and taxonomists working on Malagasy Diospyros. Figure 3 . A Screenshot of the Diospyros Lucid key -builder showing the data matrix table and the methods for scoring character data. B Inner pop-up table for numeric scores (#) of quantitative characters (here, width of largest leaf in cm) . C The 5 types of usable interpretation scores for qualitative characters colored differently depending on the level of the character’s certainty: ver ified and unambiguous (blue), possible or likely to be misinterpreted (red), rare (green), rare and prone to misinterpretation (yellow), uncertain (?). Development of the key The process of developing the Diospyros key involved making changes and fine -tuning it to enhance both its functionality and visual aspects in an effort to make it as user -friendly and straight forward as possible while retaining the ability to incorporate various types of supplementary information to improve identification accuracy. As English is the default language for Lucid, it was utilized in the development of the prototype Diospyros key. Considering the varying levels of botanical knowledge and familiarity with terminology among users in Madagascar, the key was designed to employ concise terminology for characters (features) while avoiding complex technical terms. Nevertheless, certain scientific terms were retained to maintain precision. For example, the technical term “brochidodromous” was used to define leaf venation in which s econdary veins do not terminate at the margin but join to form a series of prominent arches, which form a submarginal nerve (Ellis et al. 2009). A B C Author-formatted, not peer-reviewed document posted on 16/08/2024. DOI:  https://doi.org/10.3897/arphapreprints.e134616 12 Figure 4. A & B Screenshot from QGIS 3.16.8 C & D Screenshot of Lucid key builder. A current distribution map visualized on QGIS within Madagascar B Map of the southern part of Madagascar showing grid cells (red dashes) encompassing the potential range visualized on QGIS C some of the eco-geographic features employed (elevation and geographic coordinates) D Coordinate position coding system using the degree values of each 1 x 1 degree cell. Media tool function To augment the utility of the key, images were incorporated for each species, including photos of living plants as well as details of particular organs and distinctive features, accompanied by scans of herbarium specimens and line drawings as exemplars. Using the image viewer function of Lucid, the user can thus scrol l among images and zoom in as needed to facilitate comparison with the material being identified. Selected images were recomposed to highlight key characters and character states in the ‘features’ window, and photos were taken of informative structures from herbarium specimens (e.g., leaves, fruits, bark samples, etc.) using the high-resolution imaging equipment at the MNHN in Paris (a Nikon D7100 camera with a Nikkor AF-S 60 mm macro lens mounted on a Kaiser light stand equipped with a Cognisys StackShot Macro rail). Two methods were employed. For two-dimensional objects such as leaves, photos were taken using the macro mode in the Nikon Camera Control software (ver. 2.0), whereas for large objects such as fruits or those with significant relief (e.g., bark), z-stacking was done using the Helicon Remote program (ver. 3.9.12) and Helicon Focus (ver. 8.1.1), which creates a final image with unlimited depth of field by electronically superimposing the in-focus portions of a series of shots taken at distinct lev els and combining them into a single image that clearly shows the entire Author-formatted, not peer-reviewed document posted on 16/08/2024. DOI:  https://doi.org/10.3897/arphapreprints.e134616 13 structure being photographed. A total of ca. 4,500 images were taken from 200 bark samples representing 40 of the 88 large tree species of Diospyros (bark material was not available for the other 48 species). An integrated glossary provides quick access to clear definitions of all technical terms, often accompanied by photos and/or illustrations. The definitions presented to the user were compiled from several widely used sources, including Beentje (2016) and H arris & Harris (2001) for general terminology, and Ellis et al. (2009) for features relating to leaf architecture. The utility of the Diospyros key was further strengthened by providing links to internet sources for each species, including the corresponding pages in the Madagascar Catalogue (2024) and the IUCN Red List (2023), although these can only be accessed when connected to the internet. However, because precise information on the distribution of precious wood species is potentially sensitive, access to maps and full data on known occurrences is limited in these on-line sources and is not available to the general public. Testing the key and integrating feedback Early iterations of the Diospyros key underwent thorough evaluation and testing by botanists familiar with Madagascar's precious woods, particularly Diospyros, as well as by non-specialists. This was done during a series of working sessions in which participants provided feedback through evaluation forms. The results were utilized to enhance and fine -tune both the structure and content of the key. Subsequently, three initial trial identification workshops using herbarium specimens were held (in June and September 2021, and October 2022) fo r groups of participants with varying levels of knowledge and experience. The main objectives were to: 1) Review and discuss the multi -access structure of the key and ease of interpretation of the characters 2) Determine which of the morphological and eco-geographic characters were the most informative for making accurate species-level identifications 3) Test the overall performance of the key and identify problems or gaps In April 2022, an additional test workshop was conducted for students participating i n the Madagascar precious woods project at the University of Antananarivo, and six regional training workshops were organized between November 2022 and August 2023 for various important stakeholder groups such as customs agents, members of the judiciary po lice, police officers, forestry agents, and conservation site managers. The purpose of these workshops was to introduce the key to the participants and gather their comments and suggestions.

Results

Key efficacy, character performance, and limits During the initial test sessions, participants were able to achieve correct identifications from 65 – 75% of the time. The feedback received after each workshop was then used to make improvements to the Diospyros key. Specifically, adjustments were made rega rding the organization and structure of characters and character states. The presentation to the user was also modified based on the logical progression from basal to apical organs and from macro - to microscopic features. Additionally, the characters were re-categorized into two main groups within the key, “Morphology” and “EcoGeo”. Author-formatted, not peer-reviewed document posted on 16/08/2024. DOI:  https://doi.org/10.3897/arphapreprints.e134616 14 The results obtained from the trials indicated that the initial versions of the key were highly successful at leading users to the correct identification. The fact that the key is designed to allow multi- access utilization was clearly a strength because it enabled the users to follow their intuition when selecting the order of characters to be entered. The botanists who tested the key made several suggestions for its improvement and for how it can be used most efficiently. They first recommended that a user first note any obvious and striking features of the material being identified. For example, one of the most evident characters in fresh material of Diospyros rubripetiolata is the red tinge of the petiole, and if the user goes directly to the ‘features’ window and selects Morphology/Leaves/Petiole/Color_in_vivo/Red, the number of ‘discarded entities’ that do not express this particular character state (which is indicated in the lower left of the window) is indicated as 87, while the number of ‘remaining entities’ is indicated as 1 in the upper right, corresponding to D. rubripetiolata (Figure 5). By clicking on the first photo in the species profile, the ‘image viewer’ displays a ll 11 images corresponding to the species, several of which clearly show the red petioles, thereby rapidly facilitating verification of the identification. The second suggestion made during the test phase was that, in the absence of obvious and informative morphological characters, the user should start by focusing on eco-geographic parameters. In particular, they should begin by entering the geographic coordinates (longitude and latitude) of the location where the sample was obtained, which prov ides an efficient way to reduce the number of candidate species. For example, when one enters the coordinates corresponding to the 1˚×1˚ cell for localities with a longitude starting with 46˚E and a latitude starting with 15˚S (using the format called for in the key, ‘4615’), 74 entities are excluded and only 14 candidate species are retained (i.e., just 16% of the 88 large tree species of Diospyros occurring in Madagascar). A third suggestion was that, when using vegetative characters, leaf features should be considered first because they are often the most effective for distinguishing species from one another. For example, the cordate leaf shape of Diospyros vescoi combined with the presence of indument on both surfaces of the leaf blade are diagnostic for this species. When reproductive organs are available, the fruit is often useful and informative, especially features of the fruiting calyx, such as the degree to which it c overs the fruit surface and the presence/absence of lobes. As an example, if the initial entry of characters indicates D. mapingo and D. tropophylla as the two remaining candidate species, they can easily be distinguished based respectively on the presence or absence of lobes on the fruiting calyx. Regarding characters seen as difficult to interpret or not particularly useful or pertinent for identification in the field or the herbarium (and thus rarely chosen during testing), the participants mentioned that subjective or ambiguous features requiring the user to make a personal interpretation, such as color (for both fresh or dried material) and leaf texture, were frequently scored differently by different persons. Likewise, it can be challenging to select t he correct character state for features such as trichome type and length, which often requires using a hand lens or microscope, and is thus not always possible or practical in the field, especially for someone who is not familiar with the corresponding technical terminology. These characters are therefore more appropriate for identifying herbarium specimens and for use by experienced botanists. After incorporating user feedback and remarks to improve the overall accuracy, appearance, and user-friendliness of the Diospyros key, it is now fully operational, enabling error -free identification of species 90-100% of the time. Author-formatted, not peer-reviewed document posted on 16/08/2024. DOI:  https://doi.org/10.3897/arphapreprints.e134616 15 Figure 5. Screenshot of the deployed key in the Lucid player interface showing use of the characters that are most obvious when examining a sample with the naked eye. The example shown here assumes that the key had already been used to identify a sample taken from a tree in the field whose leaves have a red petiole. A By selecting the character state “red” for petiole color in vivo, a single candidate species is retained. B Window showing the number of selected features and the chosen path. C Window showing the numb er of remaining entities after one or more characters have been selected, in this case, the single entity corresponding to Diospyros rubripetiolata; the image viewer can be accessed by clicking on the first image displayed. D Window indicating the number of discarded entities; in this case, the 87 species that did not meet the selected identification criterion ‘red petioles in vivo’. Several practical aspects should be considered when developing and refining Lucid keys such as the one we have prepared for Malagasy Diospyros. The use of English could be an issue for some users not intimately familiar with terminology in this language. Several participants suggested during the testing phase that it would be helpful to have a vers ion in French or even in Malagasy (which would be more challenging to develop as many technical terms do not exist in this language). It would also be helpful to have a version developed for use on smartphones, which are more portable and would facilitate use at remote field sites lacking internet access. Conversion of the Lucid tool into a mobile application for Android or iOS can be done, but publication of a fully functional key would involve an additional 5 - step development phase requiring paid services that can only be provided by the Lucid team.

Conclusions

and perspectives As part of a coordinated effort to promote the sustainable and equitable use of precious woods resources in Madagascar in response to the CITES Action Plan regarding the genera Diospyros and Dalbergia, and in particular with respect to the development of practical and reliable identification tools for species that are of potential commercial interest, we have developed a key using Lucid that can be employed to identify standing and recently felled trees as well as herbarium specimens. This powerful, interactive, multi-access key can be used without an internet connection and is accessible to a broad group of users, ranging from non -specialists to experienced botanists. Moreover, s ince most trees encountered during forest inventories lack flowers and fruits, the key was designed specifically to enable accurate identification of sterile material using characters that can be observed in the field throughout the year. Special attention was given to incorporating vegetative characters, including bark features, which have been shown to be useful and informative for distinguishing Diospyros species in the field (further work is being conducted to explore the taxonomic value of bark charact ers). Eco-geographic Author-formatted, not peer-reviewed document posted on 16/08/2024. DOI:  https://doi.org/10.3897/arphapreprints.e134616 16 features were also used to develop the key and were found to be particularly valuable for increasing the speed and accuracy of identifications by returning only candidate species that are known or inferred to occur within a given 1˚×1˚ cell. The morphological and eco -geographic characters employed in our key enable accurate identification of all 88 species of Diospyros in Madagascar that form large enough trees to be potential sources of commercially valuable ebony wood. Each species is accompanied by its own set of images to help verify initial identifications, along with links to additional information available online, and most technical terms are likewise illustrated to facilitate accurate comprehension and interpretation. Lucid is a tried and tested platform that is flexible and offers many useful options, enabling regular improvements and updates, including the addition of new species and informative characters. For example, as work progresses on developing a comprehensive understanding of characters based on anatomy, spectroscopy, and even DNA barcoding of Malagasy Diospyros, taxonomically informative features can be incorporated into our key. As part of the G3D project focusing on precious woods in Madagascar, a key has also been developed for the 56 large tree species of Dalbergia from which rosewood and palisander are obtained. There remain some aspects that could be refined for further improvement of the current version of the key. Additional field testing encompassing multiple p opulations of each species (especially those that exhibit significant morphological variation) would be valuable. This could improve our knowledge of character variation, add new features while removing those that are less informative or more difficult to interpret, and fill gaps in character states for some species (notably for bark features), identifying and correcting errors that may have inadvertently been introduced into the character data matrix. After an ongoing round of improvements now being completed, the key will be translated into French to render it more accessible for francophone users and in parallel we will seek support to develop and test a stand- alone, portable version for smartphones. Finally, the methods and approach used to develop this practical identification tool for exploitable Malagasy Diospyros species could easily be expanded to include all ca. 285 members of the genus occurring on Madagascar and all 83 species of Dalbergia (Madagascar Catalogue, 202 4) as well as to other groups (genera and even families) of plants and animals of commercial and/or scientific interest. Key security and accessibility Because many of the Diospyros species harvested in Madagascar as sources of ebony wood are threatened by over -exploitation and illegal logging, information relating to their characterization and distribution is potentially sensitive. To ensure that access to and use of the prototype key presented here for identifying large tree species can be adequately controlled, we have opted to host it on a password protected server, making it available to appropriate users when a request is sent to the first author. Upon obtaining a password, the user will be able to access an html link that can be opened on any web browser, both online or offline. Author-formatted, not peer-reviewed document posted on 16/08/2024. DOI:  https://doi.org/10.3897/arphapreprints.e134616 17 Acknowledgments We are grateful to the G3D consortium, the Fondation Franklinia, and the “Bourse du Gouvernement Français” (BGF) through the French Embassy in Madagascar (SCAC) for financial support, and to the herbarium of the MNHN in Paris for providing the first author with full access to its collections. Many thanks go to the MBG field botanists in Madagascar for the collection of materials used in this study and for their beautiful field photos available in the Tropicos image gallery. Special thanks to the Atelier d’Iconographie Scientifique, UMS 2700 2AD MNHN and Didier Geffard for the use of the photographic equipment and help with the capturing and processing of images. The curators of the herbaria whose

Material

was consulted (MO, P, TAN, TEF) are gratefully acknowledged. Roger Lala Andriamiarisoa and Alain Jouy kindly provided excellent illustrations used in the key and we thank the participants in the testing workshops, who contributed much to improving the current version of the key by offering feedback and comments.

References

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