Abstract
The known arthropod vector species on the Gulf of Guinea islands belong to orders Diptera and Ixodida. Among the Diptera, the family Culicidae (mosquitoes) has the most species, 34 (6 endemic), Ceratopogonidae has 13 (all in the genus Culicoides), Tabanidae has 6, and Simuliidae has 3 (1 endemic). Ixodida has only 4 species. Most vector species and associated diseases are shared with mainland Africa. Some of these include (1) the human malaria vector Anopheles coluzzii, (2) yellow fever and dengue vector Aedes aegypti, and (3) the spotted fever group rickettsiae and Q fever vector Amblyomma spp. However, there is a considerable lack of information on the natural cycles of many vector-borne diseases that might impact local fauna, for which there may be some endemic pathogen lineages. Increased trade by air and sea should compel authorities to remain vigilant, to keep unwanted vectors and diseases at bay. Entomological diversity data remains scarce for Annobón and for the forested interior of the islands, where future sampling efforts may uncover new endemic species.
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Introduction
The discipline of medical entomology originated in the late nineteenth and early twentieth centuries (Service 1978), when P. Manson and R. Ross discovered the obligatory development of specific life stages of the human pathogenic filarial, Wuchereria bancrofti Cobbold, 1877, and avian malaria Plasmodium parasite in the mosquito Culex quinquefasciatus Say (Ross 1911). This discipline aims at studying insects and other arthropods that affect the health of humans, domestic animals, and wildlife (hereafter called vectors). Vector biology can be subdivided into medical (emphasis on human), veterinary (domestic animals), and wildlife disciplines (Edman 2009). However, these are often intertwined, since many vectors transmit infectious agents that cause similar diseases in both humans and animals (zoonoses). A large diversity of pathogens is transmitted by hematophagous arthropods (insects or ticks), including filariae (i.e., worms), protozoa (e.g., malaria), bacteria, and viruses (e.g., dengue, yellow fever, or Zika). Of all the arthropods, the Order Diptera contains the most species that transmit pathogens to humans and wildlife, including one of the most studied families, the Culicidae (mosquitoes).
Recent mosquito surveys on Comoros (Mayotte Island: Le Goff et al. 2014), Seychelles (Le Goff et al. 2012), and Mariana Islands (Guam: Rueda et al. 2011) reveal high numbers of species but few single-island endemics. By contrast, São Tomé and Príncipe harbor six endemic mosquito species (Ramos et al. 1994; Ribeiro et al. 1998; Loiseau et al. 2019) and this high level of mosquito endemism (23%) is especially unusual considering the proximity of the islands to the mainland. In comparison, the Galapagos, Hawaii, and Canary archipelagoes do not harbor endemic mosquito species (Baez 1987; Carles-Tolra 2002; Bataille et al. 2009), while the Azores and Madeira have only one each (Ribeiro and Ramos 1999). Other Dipteran families containing disease vector species, such as Simuliidae and Ceratopogonidae, have been less studied on the Gulf of Guinea oceanic islands, probably due to their lower diversity and lesser medical importance.
In this chapter, we present an overview of the known biodiversity of arthropod vectors and their associated diseases on the Gulf of Guinea oceanic islands. We describe the microhabitats of Culicidae and Simuliidae species and propose future directions that might help in documenting and describing new vector species from the archipelago.
Diversity, Endemism, and Disease Ecology
All vector species on the Gulf of Guinea oceanic islands are Diptera or Ixodida arthropods.
Class Insecta
Order Diptera
The order Diptera is composed of two suborders, Nematocera and Brachycera (Pape et al. 2011). More than 150,000 species have been described, including numerous hematophagous insects able to transmit infectious diseases. Diptera species known as vectors in the Gulf of Guinea islands belong to five families.
Suborder Nematocera
Family Culicidae
Globally, Culicidae includes 3578 mosquito species and subspecies, in 42 genera (Walter Reed Biosystematics Unit 2001). Seven hundred and ninety-five species are known to occur in the Afrotropics (i.e., 22% of the mosquito diversity; Rueda 2008). Culicidae is one of the most studied Diptera families, both worldwide and in the Gulf of Guinea oceanic islands. Hence, for this group, we detail relevant expeditions, from the early twentieth century, which relied mostly on collecting immature stages, to more recent collections, which used both immature and adult decoy trapping.
Early Expeditions (1932–1964)
Published records dating back from the Percy Sladen and Godman Trust expeditions in 1932 and 1933 (Edwards 1934) recorded five species on São Tomé (Anopheles gambiae Giles, 1902, Uranotenia micromelas Edwards 1934, Aedes nigricephalus Theobald, 1901; Culex fatigans Wiedemann, 1828 and Culex tamsi Edwards, 1934) and two on Príncipe (Aedes aegypti Linnaeus, 1762 and Eretmapodites chrysogaster Graham, 1909). Two species described from material collected on this expedition, U. micromelas and Cx. tamsi, are still considered endemic to São Tomé and Príncipe. Based on samples collected during expeditions between 1952 and 1955, 15 additional species were reported for São Tomé and Príncipe (Gãndara 1956). During the program to eradicate tsetse flies on Príncipe (see section on Tabanidae), nine species of mosquito were found, four of which were new to the islands, including Aedes (Aedimorphus) larvae that were not identified to species (Pinhão and Mourão 1961). A few years later, an intensive survey of mosquito larvae at 14 sites on São Tomé (Mourão 1964) collected five additional species (Uranotaenia balfouri Theobald, 1904, Aedes metallicus Edwards, 1912, Aedes circumluteolus Theobald, 1908, Toxorhynchites brevipalpis Theobald, 1901 and Culiseta fraseri Edwards, 1914).
Further Expeditions in the Second Half of the Twentieth Century
An updated list of Príncipe Island mosquito species, based on specimens collected during an expedition in 1986, added seven species (Ae. nigricephalus, Culex antennatus Becker, 1903, C. decens Theobald, 1901, C. nebulosus Theobald, 1901, C. quinquefasciatus Say, 1826, U. micromelas and U. principensis da Cunha Ramos, 1993) to the seven previously recorded (Ramos et al. 1989). Then, two new species were described: Toxorhynchites capelai Ribeiro, 1991 (Ribeiro 1993), and Aedes (Aedimorphus) gandarai Ramos, Capela and Ribeiro, 1994 (Ramos et al. 1994). A few years later, the list of mosquito species increased to 14 on Príncipe and 26 on São Tomé (Ribeiro et al. 1998), including 6 São Tomé endemics, and 1 endemic to both islands (Appendix). The genus Culex is represented by the most species, 14, followed by Aedes, with 6.
On São Tomé and Príncipe Islands, the only current known vector of human malaria is Anopheles coluzzii Coetzee and Wilkerson 2013, previously known as An. gambiae M form. An. coluzzii is abundant in urban and village settings in coastal areas on both islands. The lower abundance and the possible absence of An. coluzzii inland and at elevations above 200 m (Pinto et al. 2000a, b), despite an abundance of semi-permanent pools for immature development, is likely due to much lower human population densities in these areas. After intensive indoor residual spraying campaigns, which started in 2005, the overall prevalence of malaria in children under 9 years old was reduced from 30.5% to 8.3% after the first round, and to 2.1% after the second (Tseng et al. 2008; Teklehaimanot et al. 2009). Prevalence has remained low (~1%; Chen et al. 2019), but active surveillance and mosquito control to prevent malaria outbreaks is ongoing (Lee et al. 2010). The only other Anopheles species present on São Tomé, but not on Príncipe, is An. coustani Laveran, 1900; however, its role as a secondary malaria vector is not known.
Lymphatic filariasis, a human parasitic infection, is caused by nematodes (Wuchereria bancrofti Cobbold, 1887, Brugia malayi Brug, 1927 and B. timori Partono, 1977), which are transmitted through the bite of infected Ae., Cx., An. and Mansonia mosquitoes (Chandy et al. 2011). The last report of the presence of W. bancrofti on São Tomé dates from 1956 and on Príncipe from 1958 (Fraga de Azevedo et al. 1960). The insecticide spraying that led to the eradication of Glossina palpalis palpalis Robineau-Desvoidy, 1830 on Príncipe (see below), probably also impacted mosquito populations, which likely led to eliminating lymphatic filariae on that island (Fraga de Azevedo et al. 1960). Further surveillance might be needed as positive serological tests for lymphatic filariasis have been reported on São Tomé in recent years (Fan et al. 2013; WHO 2019).
Recent Surveys (Within First Quarter of the Twenty-First Century)
Collections performed by the authors on São Tomé and Príncipe in 2016, 2017, and 2019 added four species to the documented diversity (Ae. albopictus Skuse, 1894, Ae. tarsalis Edwards, 1927, U. bilineata Theobald, 1909, and U. connali Edwards, 1912). These surveys were primarily focused on collecting mosquito vectors known to transmit wildlife pathogens, especially to birds. At least eight genera of mosquitoes (Aedes, Aedeomyia, Anopheles, Culex, Coquillettidia, Culiseta, Mansonia, and Uranotaenia) can transmit avian malaria (Valkiūnas 2004). Avian malaria has had devastating effects on the endemic bird populations of Hawaii (Fonseca et al. 2000), demonstrating the pernicious nature of introduced diseases on isolated animal populations. São Tomé and Príncipe birds are not heavily infected with Plasmodium, exhibiting an average prevalence of around 12% (Reis et al. 2021); however, the birds appear to be carrying Plasmodium lineages that originate from the mainland, particularly in lowland bird populations (Reis et al. 2021). Numerous mosquito species may be vectors of avian malaria in the Gulf of Guinea oceanic islands, but their vector competence has not yet been assessed and will be an important future research direction for monitoring the population health of the endemic avifauna.
The highly anthropophilic Ae. albopictus (invasive tiger mosquito), likely introduced to the Gulf of Guinea during the last 10 years, is now very widespread on both islands and is of considerable human biting nuisance (Reis et al. 2017; Loiseau et al. 2019). Along with Ae. aegypti, Ae. albopictus is considered an urban cycle vector (Kamgang et al. 2019b) of Yellow Fever, Dengue, Zika and Chikungunya viruses, which actively circulate in neighboring African mainland countries (Paupy et al. 2010; Braack et al. 2018; Kamgang et al. 2019a). Periodic outbreaks of Yellow Fever occur in neighboring mainland countries, namely in Cameroon, Gabon, and Angola (Chippaux and Chippaux 2018). One study estimated that currently there are between 51,000 and 380,000 severe cases of yellow fever annually in Africa, resulting in an estimated 19,000–180,000 deaths (Garske et al. 2014). Dengue virus strains, in the same Flavivirus genus as Yellow Fever virus (Daep et al. 2014), are now probably one of the most important arboviruses, since globally they infect over 100 million people annually, resulting in an estimated 500,000 severe Dengue cases (WHO 2014). A serological survey on pregnant women has actually demonstrated the circulation of this virus on the islands (Yen et al. 2016). No major outbreak of Dengue has been recorded on the islands until a recent one in São Tomé in 2022. In addition, nine resident mosquito species found in São Tomé and Príncipe (Ribeiro et al. 1998) are known as vectors of numerous other arboviruses (e.g., Alphavirus, Flavivirus, or Phlebovirus) in the Afrotropics.
Currently, both Anophelinae and Culicinae subfamilies are present in the Gulf of Guinea islands, as well as the only Culicidae genus that is endemic to Africa, Eretmapodites Theobald, 1901. There are 35 resident Culicidae species: 31 on São Tomé and 15 on Príncipe (Appendix). To our knowledge Ae. indet (Pinhão and Mourão 1961) has not been collected in the last 70 years, and its current presence on the islands is questionable. We have not included An. funestus s.l. Giles, 1900, An. paludis Theobald, 1901, and An. pharoensis Theobald, 1901 (Mesquita 1946, 1952) in the current list of species, because malaria control campaigns in the 1980s are thought to have eradicated them (Pinto et al. 2000a). The only publication on the mosquitoes of Annobón was about malaria transmission and genetic population structure of An. coluzzii in Equatorial Guinea (Moreno et al. 2007).
Family Simuliidae
Among the 2200 species of black flies described around the world, 214 are present in the Afrotropical region (Currie and Adler 2008), including many that transmit pathogens that affect humans (e.g., filarial disease onchocerciasis; Crosskey 1990), poultry (Alder and McCreadie 2019), and wild birds (Valkiūnas et al. 2004). Onchocerciasis (river blindness) is limited to sub-Saharan Africa and is widely known in southern Cameroon and on Bioko Island, where it is transmitted by species of the complex Simulium damnosum Theobald, 1903 (Post et al. 2003). Currently, this vector species does not occur on the Gulf of Guinea oceanic islands (Mustapha et al. 2004), and no cases of Onchocerciasis have been reported. The avian parasites Leucocytozoon, closely related to avian malaria, are present, especially in highland and forest birds of São Tomé and Príncipe (Reis et al. 2021). However, the vector competence of black fly species for Leucocytozoon spp. remains unknown on the islands.
Black flies were first documented at one site on São Tomé in 1988 (Grácio 1988). Extensive sampling of 71 sites on São Tomé reported the presence of two species: Simulium (Pomeroyellum) alcocki Pomeroy, 1922, and S. (Anasolen) dentulosum Roubard, 1915, the latter being the most abundant (Grácio 1999). In 1998, the São Tomé endemic S. (Pomeroyellum) santomi Mustapha, 2004 was added to the list (Mustapha et al. 2004). On Príncipe, only S. dentulosum is confirmed. No effort has been made to sample black flies on São Tomé or Príncipe during the last 20 years, and it has been suggested that they are absent from Annobón (Mustapha et al. 2004).
Family Ceratopogonidae
This family of biting midges includes 6206 species in 112 genera and has a diverse fossil record (around 300 species; Borkent and Dominiak 2020). Many species of Ceratopoginidae are important pollinators, and only four genera are known to have species that feed on blood of vertebrates, including humans (Borkent 2004): Austroconops Wirth and Lee, 1958, Culicoides Latreille, 1809, Forcipomyia (subgenus Lasiohelea) Meigen, 1818 and Leptoconops Skuse, 1889. Austroconops is the only genus that is not known to play a role in pathogen transmission, while Culicoides is the most important in this regard (Borkent 2004). Culicoides includes 1347 described species, and the assessment of this diversity has received much attention in Africa because of their status as vectors of human filarial nematodes (Agbolade et al. 2006), and of several viruses responsible for animal diseases, such as Bluetongue (Mellor 1990) and African Horse Sickness (Mellor et al. 2000; Mellor and Hamblin 2004). Culicoides are also known vectors of avian malaria-like parasites of the genera Haemoproteus (Parahaemoproteus) and Leucocytozoon (Caulleryi) (Valkiūnas 2004). On São Tomé, approximately 20% of the birds are infected with these parasites, with a higher prevalence in shaded plantations (Reis et al. 2021). Among the species of Culicoides, several can transmit Haemoproteus, but vector competence of Culicoides species remains unknown.
The first four species of Culicoides recorded on São Tomé were collected during the Percy Sladen and Godman Trust expeditions in the 1930s (Edwards 1934), and identified as C. austeni Carter, Ingram and Macfie, 1920, C. distinctipennis Austen, 1912, C. citroneus Carter, Ingram and Macfie, 1920 and C. grahamii Austen, 1909. A three-year study of insects in cocoa plantations identified 25 species of Ceratopogonidae, including only one Culicoides species: C. imicola Kieffer, 1913 (Wirth and Derren 1976). This fifth species recorded on the island is a known primary vector of Bluetongue and African Horse Sickness viruses, largely distributed in Africa, Asia, and Europe (Guichard et al. 2014). C. distinctipennis, C. milnei Austen, 1909 and C. imicola were later mentioned as present on São Tomé (Glick 1990), the latter being the sixth Culicoides species recorded on the island. Since the mid-1970s, there has been no evaluation of the diversity of Culicoides on São Tomé and Príncipe Islands, and the number of species is thus likely underestimated. There are 156 species formally described in the Afrotropical region (Labuschagne 2016), including high diversities on neighboring mainland African countries, such as Nigeria (Dipeolu 1976) and Cameroon (Callot et al. 1965; Wanji et al. 2019). Gabon is an exception since only six species have been described so far, probably due to very few studies carried out in that country (Delécolle et al. 2013; Augot et al. 2017). In 2019, nine species of Culicoides were found in the southeast of São Tomé, along transects from the center of an oil palm plantation to the native forest. While morphological and molecular investigations are ongoing, it is likely that seven species will be added to the records for the island (Appendix). From the four species first recorded for the island (Edwards 1934), only C. citroneus and C. distinctipennis were found recently. Surprisingly, no endemic Culicoides species have been found yet. Considering sampling bias in these islands, it is likely that future studies in different habitat types, especially deeper in the native forest, or in coffee and cocoa plantations, will reveal the presence of endemic Culicoides species. Future surveys will most certainly also increase the number of Culicoides species on Príncipe and Annobón, as well as clarify their ecology.
Suborder Brachycera
Family Tabanidae
Worldwide, there are currently close to 4400 species and subspecies, and 144 genera of Tabanidae described (Mullens 2019). Tabanid flies of the genera Tabanus, Chrysops, and Hybomitra, commonly known as horseflies and deerflies, are of economic, medical, and veterinary importance (Nevill et al. 1994). However, they tend to be less studied than other Dipteran families (Baldacchino et al. 2014). Tabanid flies serve as biological vectors (pathogens replicate and develop within the fly), and as mechanical vectors (pathogens are transmitted without amplification and development within the fly via contaminated blood on mouthparts) of several wildlife and livestock pathogens, such as Trypanosoma spp. (Nevill et al. 1994), Babesia spp., and Theileria spp. (Taioe et al. 2017), filarial nematodes, and numerous viruses and bacteria (Baldacchino et al. 2014). In forested Central Africa, tabanid flies of the genus Chrysops also infect humans with Loa loa Cobbold, 1864, which causes African eye worm (Mullens 2019). This pathogen has not been reported in São Tomé and Príncipe.
Six species in the genus Tabanus have been recorded on São Tomé and Príncipe: T. biguttatus Wiedemann, 1830; T. congoiensis Ricardo, 1908; T. obscurefumatus Surcouf, 1906; T. taeniola, Palisot de Beauvois, 1806; T. principis Bequaert, 1930 (Bequaert 1930) and T. monocallosus (Travassos Santos Dias 1955), the last two being endemic to the Gulf of Guinea islands. No new tabanid flies have been recorded on the archipelago in recent years.
Family Glossinidae
Glossinidae includes the single genus Glossina with 23 species, 6 of which are further divided into 14 subspecies, all but one found in Africa (Krinsky 2019). The genus is divided into three groups based on their ecological preferences: the savannah flies (subgenus Morsitans), the forest flies (subgenus Fusca), and the riverine flies (subgenus Palpalis). Species found in sub-Saharan Africa are vectors of the Trypanosoma parasites that cause sleeping sickness in humans (Welburn et al. 2001) and trypanosomosis in livestock (Meyer et al. 2016) and can have severe impacts on domestic cattle production (De Geier et al. 2020).
The first known introduction of the tsetse fly, G. p. palpalis, occurred on Príncipe Island in 1825 (Fraga de Azevedo et al. 1956). At the end of the nineteenth century and beginning of the twentieth century, it became a significant health issue for cocoa plantation workers and local inhabitants, forcing important prophylactic measures between 1911 and 1914, which included hunting for flies, swamp drainage, clearance of vegetation and slaughter of wild pigs, stray dogs, and civets (Bruto da Costa 1913). The prevalence of Trypanosoma dropped dramatically (Bruto da Costa 1913), and in 1914 the tsetse fly was considered eradicated in Príncipe (Figueiredo Moura da Silva 2019). In 1956, entomologists rediscovered large numbers of tsetse fly on Príncipe (Tendeiro 1956) and suggested it had been reintroduced from Bioko Island. Although no cases of trypanosomiasis were found in humans, animals or in the tsetse flies, important measures were applied again to eradicate the tsetse flies, including trapping flies, insecticide spraying, clearing of vegetation, and killing of wild pigs, monkeys, and dogs (Fraga de Azevedo et al. 1956). Eradication was effective by July 1958.
Order Siphonaptera
Two flea species, Ctenocephalides felis Bouché, 1935 (cat flea; Family Pulicidae) and Tunga penetrans Linnaeus, 1758 (chigoe flea; Family Tungidae), occur in São Tomé and Príncipe. A high percentage of dogs seem to have cat fleas infected with Rickettsia felis, an emerging human pathogen often causing febrile illness, while just over 3% of humans had antibodies against this bacterium (Tsai et al. 2020).
Class Arachnida
Order Ixodida
The Ixodida contains three families: Ixodidae, Argasidae, and Nuttalliellidae (Nicholson et al. 2019). The Ixodidae or hard-bodied ticks include 15 genera and 707 species, while the Argasidae or soft-bodied ticks contain about 190 species, and the Nuttalliellidae only one species. Worldwide, they are the most important disease vectors in the veterinary field and are second only to mosquitoes in public health importance (Nicholson et al. 2019). Ticks are ectoparasites that blood-feed on mammals, birds, reptiles, and amphibians, but unlike the short blood-feeding periods (at most a few minutes) of Diptera, hard-bodied ticks attach and stay on their hosts for several days. They are implicated in the transmission of numerous infectious diseases caused by pathogens, such as bacteria (e.g., Rickettsia, Borrelia, Coxiella; Parola et al. 2013), viruses (e.g., Crimean–Congo hemorrhagic fever virus, Tick-borne encephalitis virus; Hoogstraal 1979) and protozoa (e.g., Babesia; Nelder et al. 2016).
Family Ixodidae
Four species of hard-bodied ticks have been recorded through the years from São Tomé and Príncipe. Amblyomma astrion Dönitz, 1909 and A. splendidum Giebel, 1877, were collected on São Tomé, and A. splendidum on Príncipe (Tendeiro 1957). Subsequently, Rhipicephalus decolaratus (Koch, 1844) was collected on both islands (Travassos Santos Dias 1988). In the early 1980s, numerous adult cow and calf deaths on São Tomé were attributed to neurological complications, likely caused by heartwater, a tick-borne rickettsial disease of domestic and wild ruminants transmitted by A. astrion (Uilenberg et al. 1982). In 2016, A. variegatum Fabricius, 1794, was collected from cattle in the Agua Grande district on São Tomé (Hsi et al. 2020). A serological survey demonstrated the presence of Spotted fever group rickettsiae and Q fever (Coxiella burnetti) antibodies in people, which could explain continued reports of febrile illness in São Tomé human residents not due to malaria (Hsi et al. 2020).
Family Argasidae
To date, Ornithodoros capensis Neumann, 1901 is the only soft tick species reported for the islands (Travassos 1988). It is an ectoparasite of seabirds in the tropics and subtropics, and was collected in the nests of Brown Noddy Anous stolidus (Linnaeus, 1758), Black Noddy A. minutus (Boie 1844), and Sooty Tern Onychoprion fuscatus (Linnaeus, 1766), during an expedition to Tinhosas (small islets south of Príncipe) in 1970 (Travessos 1988). A recent census of seabird nests on these islets did not report ectoparasites (Valle et al. 2016; Bollen et al. 2018), but they may not have explicitly searched for them.
Distribution, Biology, and Habitat Specificity
In this section, we describe the habitat types and preferred environmental conditions of Culicidae and Simuliidae species, based on the observations of AJC and on the literature (Mourão 1964; Grácio 1999).
Mosquito Habitat and Distribution on São Tomé and Príncipe
Anthropophilic Mosquitoes
Mosquito species that regularly blood-feed on humans include disease vector species – Ae. aegypti (Fig. 15.1.1), Ae. albopictus (Fig. 15.1.2), An. coluzzii (Fig. 15.1.5), Cx. quinquefasciatus, and Ae. circumlutelous – and species not implicated as disease vectors – Ae. nigricephalus and E. chrysogaster (Fig. 15.1.3).
Immatures of An. coluzzii, vectors of malaria, are found mostly on the coast. They develop in direct contact with clear or eutrophic groundwater, in swamps, and in temporary pools, such as in roadside ditches, depressions in pathways, and between households (Fig. 15.2.1). Blood index values and low sporozoite rates in An. coluzzii sampled in 1997 and 1998 on São Tomé (Sousa et al. 2001) indicate that they are meso-endemic, feeding predominantly on dogs, followed by humans, and then pigs. In recent collections by AJC, An. coluzzii were also attracted to chicken.
Cx. quinquefasciatus (Cx. fatigans in Mourão 1964), a vector of filarial nematodes, is very common in urban areas. It bites humans at night inside homes, and often rests indoors or underneath houses along with Anopheles mosquitoes. They represent the majority of mosquitoes in the city of São Tomé (Mourão 1964). Immatures of Cx. quinquefasciatus are often found in very high numbers in unmaintained sewage systems and in artificial containers, such as barrels, gutters, tubs, or vats of water.
Ae. aegypti and Ae. albopictus, vectors of numerous viruses, primarily bite humans during the day. They have spread worldwide and become cosmopolitan (Paupy et al. 2009; Brown et al. 2011; Kraemer et al. 2019). Historically, they both laid eggs in tree cavities (e.g., Erythrina sp., Chlorophora sp.), but now they are considered container-breeding mosquitoes, as immatures often develop in discarded plastics, tires, and other rubbish that hold water, and in unused cisterns. Still, both species lay eggs in the abundant supply of tree cavities, as well as in fallen banana leaves, in São Tomé and Príncipe. In the past, Ae. aegypti was the most collected species (Mourão 1964), but its abundance seems to have decreased since Ae. albopictus became established in São Tomé and Príncipe (Reis et al. 2017), as in other parts of the world (Bargielowski and Lounibos 2016). The distribution of Ae. aegypti has now contracted into small enclaves, mostly at higher elevations on São Tomé, and is rarely collected on Príncipe.
Ae. circumluteolus is localized and infrequently captured (human-biting at Mucumbli, São Tomé), and represents the only typical floodwater Aedes species on São Tomé, even though immatures have been found in ground pools and in artificial containers (Mourão 1964). This species is a known vector of significant arboviruses, such as Rift Valley Fever, Wesselsbron, Bunyamwera, and Pongola viruses in Africa (Braack et al. 2018).
Finally, E. chrysogaster, another pernicious daytime human blood-feeding mosquito, lays eggs opportunistically in trash, but mostly in natural containers, such as plant leaf axils, especially in fallen banana and palm leaves, or cocoa and coconut shells. This species is present everywhere on the islands but is not known to transmit diseases in São Tomé and Príncipe.
Opportunistic Mosquitoes
Ae. nigricephalus, an opportunistic blood feeder, bites humans during the day and does not disperse far from brackish water estuaries and mangroves, where immatures develop in crab holes. Cx. cinerellus Edwards, 1922 is also specialized to develop in brackish water crab holes (Hopkins 1952).
Immatures of other abundant mosquito species, which are more likely to feed on birds, and only seldom feed on humans, such as Cx. decens, Cx. antennatus, and Lutzia tigripes (de Grandpré & de Charmoy, 1901) also occur in temporary water bodies. Cx. decens can be abundant on São Tomé (Mourão 1964), and its larvae were frequently found in artificial containers. On Príncipe, large numbers of larvae were found along slow-moving rivers (Fig. 15.2.2).
Immatures of other species that seldom bite humans (e.g., Ae. tarsalis, Ae. gandarai, Culex macfiei Edwards, 1923, Cx. nebulosus) and nectar feeders (Toxorhynchites capelai and T. brevipalpis; Fig. 15.1.4), develop in tree holes and less so in banana or plant leaf axils. Rotting coconut fruits serve as significant sites for the development of Cx. (Culiciomyia) nebulosus, while adults primarily rest in crab holes (Fig. 15.2.3). Interestingly, immatures of Cx. cambournaci Hamon & Gandara, 1955 are often found in large numbers in the flowers of Heliconia species, which have been introduced from the neotropics as ornamentals (Fig. 15.2.4).
The immatures of other species including Cx. annulioris Theobald, 1901, Cx. invidiosus Theobald, 1901, Cx. thalassius Theobald, 1903, Cx. tamsi, Culiseta fraseri, L. tigripes, Ur. capelai, Ur. principensis, Ur. balfouri Theobald, 1904, Ur. bilineata and Ur. connali are typically found in river seepages, and rocky and thickly vegetated vernal pools. All these opportunistic mosquitoes are potential vectors of avian Plasmodium.
Black Fly Habitat and Distribution on São Tomé
Immature Simuliidae filter-feed in flowing waterways. Stream size, water velocity, and seston load are important factors that influence the distribution of black-fly species (Palmer and Craig 2000; Adler and McCreadie 2019). Interestingly, S. alcocki and S. dentulosum are not concomitant on São Tomé (Grácio 1999), S. alcocki is restricted to the northern interior part of the island, while S. dentulosum was more widespread. Their niches tend to show ecological allopatry with S. dentulosum found in rivers from sea level to 400 m, while S. alcocki occurs from 200 to 900 m above sea level. S. alcocki immatures tend to be restricted to the first 10 cm of the water column, whereas S. dentulosum are found anywhere from close to the surface to 50 cm below the surface. Finally, S. dentulosum seems to prefer streams or rivers with weak water flow (78 cm/s, 87% of oxygen on average), contrary to S. alcocki which prefers faster water flow (122 cm/s, 98% of oxygen on average; Grácio 1999). Re-sampling the same sites would be ideal to evaluate if the habitat and microhabitat specificity of these two species have changed over time. We suspect S. alcocki as the main vector of Leucocytozoon spp. in birds, since both vectors and parasites are found in greater abundance at higher elevations.
Directions for Future Disease Insect Vector Research
Sampling Effort in Diverse Habitats and Specific Vector Families
Among all expeditions and surveys that aimed to collect vectors, we discern two major sampling paucities. First, the forested interior of São Tomé, in the Obô Natural Park, and the forested south of Príncipe are poorly studied. The main reason is probably accessibility, since reaching remote native forest requires long walks and camping. While mosquitoes have been quite well sampled along the entire coast, and also in some parts of the interior of the islands, other families such as Ceratopogonidae or Tabanidae have been sampled in few sites, and do not include all habitat types found on the islands. Second, Annobón has been poorly sampled for all groups. Although the island is small (17 km2) and more isolated, we estimate that some of its arthropod vectors are not yet described. We believe that the Gulf of Guinea oceanic islands are still full of surprises and that all three islands have the potential to hold undescribed arthropod vectors.
Surprisingly, there are no records of louse flies (family Hippoboscidae) and sand flies (family Psychodidae, subfamily Phlebotominae) on the islands. Louse flies, also known as bird flies, flat flies, or ked flies (Reeves and Lloyd 2019), are vectors of Haemoproteus parasites in Columbidae birds (Valkiūnas 2004), which have been detected in the blood of Columba larvata and C. malherbii, both on São Tomé and Príncipe (Loiseau et al. 2017; Reis et al. 2021). Thus, the presence of louse flies on São Tomé and Príncipe islands is highly suspected, even though no record has been published yet. Collection of louse flies can only be done on live birds, or by checking livestock coats. It is also somewhat surprising that no sand fly species have been found on any of the islands, although no surveys have specifically searched for them. Surveys should be done preferentially during the rainy season since these insects are highly seasonal, with abundance peaks during or right after rain (Munstermann 2019). Leishmania parasites, transmitted by sand flies, are present in Central Africa (Alvar et al. 2012) but have never been reported on the islands, supporting the hypothesis that these vectors might be absent.
New Complementary Tools to Evaluate Vector Diversity
Skilled entomologists can identify species morphologically, if they have access to updated descriptions and identification keys (Hajibabaei et al. 2007). Distinguishing characters, especially subjective ones that are used in identification keys, at the different stages (i.e., eggs, larvae, and adult specimens) are perceptively difficult for non-experts, particularly in the tropics where the diversity is often high and many species are similar. Recent developments in molecular identification techniques, coupled with reduced sequencing costs can help overcome these identification difficulties, and even reveal cryptic biodiversity. Identification of species using metabarcoding approaches on environmental DNA (eDNA) (Boerlijst et al. 2019; Krol et al. 2019) and on bulk samples (Batovska et al. 2018) is an appealing option, but it is worth noting that sequences belonging to unknown taxa are still a common problem in eDNA barcoding. Surveys of mosquito diversity using these techniques require a sound reference database, which in turn demands a considerable amount of a priori taxonomic work. This can be achieved by sequencing samples from the field and from natural history museums that have been identified by experienced entomologists.
Because dipping methods traditionally used to survey larvae may not always reflect adult diversity found with traps, determining and comparing species diversity across different types of samples (water, soil, or bulk samples) using metabarcoding might be a useful complementary approach. eDNA and bulk sample metabarcoding also show a high potential to become helpful monitoring tools to evaluate changes in relative abundance and species diversity in relation to habitat change and to detect invasive vector species in routine surveys. In addition, novel trap designs as well as visual and chemical lures to attract insects, including vector species, are always under development and may also increase surveillance and biodiversity determinations.
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Acknowledgments
We sincerely thank Branca Maria do Nascimento Rolão Moriés for searching for old journals and articles in the historical archive center at the University of Lisbon. We thank Diego Santiago-Alarcon and Kevin Njabo for their comments and suggestions that enhanced the clarity of our chapter. This work is funded by National Funds through FCT - Foundation for Science and Technology under the IF/00744/2014/CP1256/CT0001 Exploratory Research Project (CL) and the PTDC/BIA-EVL/29390/2017 DEEP Research Project (CL).
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Appendix
Appendix
List of the arthropod vectors of the Gulf of Guinea Oceanic Islands of Príncipe (P) and São Tomé (ST).
Entomological data are almost non-existent for Annobón. Beside the record of Anopheles coluzzii on Annobón, and the absence of Simuliidae, we cannot state if other vector species are present or absent. Status of each species was defined as resident (R), endemic (E), introduced (I), or no data (?)
Higher Taxonomy | Subgenus/Group | Species | P | ST |
---|---|---|---|---|
ORDER DIPTERA | ||||
Family Culicidae | ||||
Anopheles Meigen, 1818 | Anopheles | Anopheles coustani Laveran, 1900 | R | |
Cellia | Anopheles coluzzii (Anopheles gambiae M form) Coetzee & Wilkerson, 2013 | R | R | |
Aedes Meigen, 1818 | Aedimorphus | Aedes nigricephalus Theobald, 1901 | R | R |
Aedes sp. indet | E | |||
Catageomyia | Aedes tarsalis Edwards, 1927 | R | ||
Polyleptiomyia | Aedes gandarai Ramos, Capela & Ribeiro, 1994 | E | ||
Neomelaniconion | Aedes circumluteolus Theobald, 1908 | R | ||
Stegomyia | Aedes aegypti Linnaeus, 1762 | R | R | |
Aedes albopictus Skuse, 1894 | I | I | ||
Culex Linnaeus 1758 | Culex | Culex annulioris Theobald, 1901 | R | |
Culex antennatus Becker, 1903 | R | R | ||
Culex decens Theobald, 1901 | R | R | ||
Culex invidiosus Theobald, 1901 | R | |||
Culex quinquefasciatus Say, 1826 | R | R | ||
Culex tamsi Edwards, 1934 | E | |||
Culex thalassius Theobald, 1903 | R | |||
Culiciomyia | Culex cambournaci Hamon & Gãndara, 1955 | E | ||
Culex cinerellus Edwards, 1922 | R | |||
Culex macfiei Edwards, 1923 | R | |||
Culex nebulosus Theobald, 1901 | R | |||
Eumelanomyia | Culex inconspicuosus Theobald, 1908 | R | R | |
Culex rima Theobald, 1901 | R | |||
Culex micolo Ribeiro, Cunha Ramos & Capela, 1998 | E | |||
Culiseta Felt, 1904 | Theomyia | Culiseta fraseri Edwards, 1914 | R | |
Eretmapodites Theobald, 1901 | Eretmapodites chrysogaster Graham, 1909 | R | R | |
Lutzia Theobald, 1903 | Metalutzia | Lutzia tigripes De Grandpré & De Charmoy, 1900 | R | R |
Toxorhynchites Theobald, 1901 | Afrorhynchus | Toxorhynchites capelai Ribeiro, 1993 | E | |
Toxorhynchites brevipalpis conradti Gruenberg, 1907 | R | |||
Uranotaenia Lynch Arribálzaga, 1891 | Pseudoficalbia | Uranotaenia capelai Ramos, 1993 | E | |
Uranotaenia micromelas Edwards, 1934 | E | E | ||
Uranotaenia principensis Ramos, 1993 | E | |||
Uranotaenia | Uranotaenia balfouri Theobald, 1904 | R | ||
Uranotaenia bilineata Theobald, 1909 | R | |||
Uranotaenia connali Edwards, 1912 | R | |||
Family Simuliidae | ||||
Simulium Latreille, 1802 | Pomeroyellum | Simulium alcocki Pomeroy, 1922 | R | |
Simulium santomi Mustapha, 2004 | E | |||
Anasolen | Simulium dentulosum Roubard, 1915 | R | R | |
Family Ceratopogonidae | ||||
Culicoides Latreille, 1809 | – | Culicoides citroneus Carter, Ingrain et Macfie, 1920 | ? | R |
Subgenus Avaritia | Culicoides grahamii Austen, 1909 | ? | R | |
Culicoides imicola Kieffer, 1913 | ? | R | ||
Culicoides trifasciellus Goetghebuer, 1935 | ? | R | ||
Subgenus Meijerehelea | Culicoides distinctipennis Austen, 1912 | ? | R | |
Subgenus Remmia | Culicoides enderleini Cornet & Brunhes, 1994 | ? | R | |
Group Milnei | Culicoides austeni Carter, Ingram and Macfie, 1920 | ? | R | |
Culicoides hortensis Khamala, 1991 | ? | R | ||
Culicoides krameri Clastrier, 1958 | ? | R | ||
Culicoides milnei Austen, 1909 | ? | R | ||
Culicoides quinquelineatus Goetghebuer, 1934 | ? | R | ||
Group Neavei | Culicoides neavei Austen, 1912 | ? | R | |
Group Nigripennis | Culicoides sp. | ? | R | |
Family Tabanidae | ||||
Tabanus Linnaeus 1758 | Group Tabanini | Tabanus biguttatus Wiedemann, 1830 | R | |
Tabanus congoiensis Ricardo, 1908 | R | |||
Tabanus obscurefumatus Surcouf, 1906 | R | |||
Tabanus taeniola, Palisot de Beauvois, 1806 | R | |||
Tabanus principis Bequaert, 1930 | E | |||
Tabanus monocallosus Travassos Dias, 1955 | E | |||
ORDER IXODIDA | ||||
Family Ixodidae | ||||
Amblyomma Koch, 1844 | Amblyomma astrion Dönitz, 1909 | R | ||
Amblyomma splendidum Giebel, 1877 | R | R | ||
Amblyomma variegatum Fabricius, 1794 | R | |||
Family Argasidae | ||||
Ornithodoros Koch, 1837 | Subgenus Alectorobius | Ornithodoros capensis Neumann, 1901 | * |
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Loiseau, C. et al. (2022). Diversity and Distribution of the Arthropod Vectors of the Gulf of Guinea Oceanic Islands. In: Ceríaco, L.M.P., de Lima, R.F., Melo, M., Bell, R.C. (eds) Biodiversity of the Gulf of Guinea Oceanic Islands. Springer, Cham. https://doi.org/10.1007/978-3-031-06153-0_15
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