A wide range of edible insects is harvested from the wild by local communities across Africa as a traditional source of food and seasonal income (Van Huis, 2020), of which 472 species of Lepidoptera, Orthoptera, Coleoptera, Isoptera, Hymenoptera, Heteroptera, Homoptera, and Diptera have been recorded (Jongema, 2017; Van Huis, 2020). The order Lepidoptera includes 146 edible species consumed in Africa, of which more than half are in the family Saturniidae (Jongema, 2017), As of 2017, at least 80 species of Saturniidae were harvested and consumed across the continent at the caterpillar stage, largely depending on their geographic distribution and natural availability (Latham et al., 2023). For example, the utilization of Antherina suraka, Bunaea aslauga, Ceranchia apollonia, Maltagorea auricolor and Maltagorea fusicolor is documented only in east Africa, Holocerina guineensis and Imbrasia obscura are recorded only in central Africa, Cirina butyrospermi was recorded only in West Africa, whereas other species such as Bunaea alcinoe, Cirina forda, Micragone cana, Nudaurelia nyassana, Pseudimbrasia deyrollei, Rohaniella pygmaea and Usta terpsichore are common across sub-Saharan Africa (Badanaro et al., 2014; Kusia et al., 2021; Latham et al., 2023). In southern Africa, the caterpillars of Gonimbrasia belina, commonly known as “mopane worms” due to mostly occurring in the native Colophospermum mopane woodlands that extend from southern Angola to northern Mozambique, are among the most consumed insects in the region (Gondo et al., 2010; Nikodemus et al., 2023; Stack et al., 2003; Thomas, 2013).
Mopane worms are highly effective herbivores that seem to play a significant role in shaping the mopane savanna ecosystem, although this ecological dimension has received limited attention (de Swardt et al., 2018). The frass of mopane worms contributes to nutrient cycling in mopane woodlands as it contains several-fold more nitrogen, potassium, and phosphorus than leaf litter (de Swardt et al., 2018). In South Africa, game farmers in the Limpopo province (situated in the northern part of the country) believe that the defoliation of C. mopane by mopane worms increases the nutritional quality of the second flush of leaves, resulting in better forage for other animals (Sekonya et al., 2020).
Mopane worms are mostly harvested at the late instars and larger sizes by rural communities for direct consumption and trade (Hlongwane et al., 2020; Hope et al., 2009; Sekonya et al., 2020; Thomas, 2013). In the past, mopane worms were locally harvested and consumed, representing a valued contribution to rural diets as they contain three times more protein (~ 56.9 g/100 g) than beef or chicken (Hlongwane et al., 2020; Musundire et al., 2016; Numbi Muya et al., 2022), as well as more calcium, iron, zinc, and less fat compared to conventional livestock (Musundire et al., 2016). Over the past two decades, the demand for mopane worms in southern Africa increased dramatically, accompanying population growth and the movement of large numbers of people from rural areas to urban centers. In consequence, the use of mopane worms shifted from small-scale local harvesting and consumption to rural trade economies. For example, mopane worm harvesters in Limpopo may sell over 60% of their yield through formal or informal trade (Baiyegunhi & Oppong, 2016). The mopane worm trade has expanded spectacularly from its original range of local markets to a cross-border trade valued in millions of dollars (Baiyegunhi & Oppong, 2016). In 2014, the cross-border trade between Botswana, South Africa and Zimbabwe was estimated at US$4 million to US$6 million (Makhado et al., 2014). More recent data indicate that the trade of mopane worms has increased to an excess of US$85 million (Grabowski et al., 2020).
The high demand and large-scale commercialization of mopane worms have led to reports of overharvesting in Botswana, Namibia, South Africa and Zimbabwe (Mogomotsi et al., 2018; Sekonya et al., 2020). Factors such as the destruction of mopane woodland (e.g. through felling of trees for firewood) have also been pointed as a source of population decline (Mugari et al., 2019; Ndlovu et al., 2019; Sekonya et al., 2020; Togarepi et al., 2020). Perceptions of population decrease are not a recent phenomenon, as reports of the disappearance of mopane worms from parts of these countries date back over two decades (Illgner & Nel, 2000). In Botswana, a decline in the availability of mopane worms in communal areas where they were usually harvested was reported, and overharvesting and climate change were held responsible (Mogomotsi et al., 2018). In Zimbabwe, the number of mopane worms and harvest yield showed a significant drop from 2006 to 2016 due to the reduction of mopane woodlands (Ndlovu et al., 2019). Although some conservation measures such as sustainable harvesting practices exist in Botswana and South Africa, commercial harvesters do not always comply (Mogomotsi et al., 2018; Sekonya et al., 2020). Moreover, the harvesting of mopane worms is largely untraceable, contributing to concerns about the long-term sustainability of the species under increasing pressure.
Despite the socio-economic, cultural, and ecological relevance of G. belina, the genetic diversity and phylogeographical structure of the species is largely unknown. A previous study showed that G. belina is phylogeographically structured over long distances, and identified mitochondrial markers useful for assessments of the species in southern Africa (Langley et al., 2020). However, the study was limited to a small number of specimens collected in Namibia and South Africa, and the results were based on a short fragment of the mitochondrial cytochrome c oxidase subunit 1 gene (COX1; 709 bp). Our study aims at gaining further insights into the genetic diversity, phylogeographic structure and demographic history of G. belina based on expanded mitochondrial and nuclear data for specimens collected in Namibia and the Limpopo River Basin (South Africa and Botswana).