Italy was declared malaria-free by the World Health Organization (WHO) fifty years ago. Like many European countries, Italy gradually eliminated malaria outbreaks by draining wetlands where mosquitoes breed, using insecticides and window screens, and offering antimalarial drugs.
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However, new research reports on the collaborative activities conducted by the Experimental Zooprophylactic Institute of Puglia and Basilicata and the Istituto Superiore di Sanit have been able to document the presence of potential malaria vectors, such as An. labranchiae, Anopheles superpictus Grassi, 1899 and An. algeriensis in Italy's Apulia and Basilicata regions.
This notable rediscovery in the coastal areas of southeastern Italy enabled researchers to reintegrate An. sacharovi in the Italian Culicidae fauna. Adults of An. sacharovi were found indoors, resting in animal shelters or landing on humans at dusk.
These researchers wrote on April 10, 2024, 'Beyond these findings, it is necessary to underline the importance of strengthening and maintaining constant surveillance of residual anophelism, especially in vulnerable areas where sporadic malaria transmission could be possible.
'Although vector densities do not currently appear to be epidemiologically relevant enough to pose a health threat (in 2024), the conditions for a renewal of transmission in several Mediterranean countries still exist, as reported in Greece in 2011.'
Anopheles sacharovi, a member of the Anopheles maculipennis complex, was a historical malaria vector in Italy, no longer found since the last report at the end of 1960s. In September 2022, within the Surveillance Project for the residual anophelism, a single specimen of An. maculipennis sensu lato collected in Lecce municipality (Apulia region) was molecularly identified as An. sacharovi. This record led to implement a targeted entomological survey in September 2023.
Investigation was conducted in the areas around the first discovery, focusing on animal farms, riding stables and potential breeding sites. Adult and immature mosquitoes were collected, using active search or traps, in several natural and rural sites. Mosquitoes belonging to An. maculipennis complex were identified morphologically and molecularly by a home-made routine quantitative polymerase chain reaction (qPCR) assay, developed specifically for the rapid identification of An. labranchiae, and, when necessary, by amplification and sequencing of the ITS-2 molecular marker.
The discovery of An. sacharovi, considered to have disappeared from Italy for over 50 years, has a strong health relevance and impact, highlighting an increase in the receptivity of the southern areas. As imported malaria cases in European countries are reported every year, the risk of Plasmodium introduction by gametocyte carriers among travellers from endemic countries should be taken into greater consideration. Our findings allow rethinking and building new models for the prediction and expansion of introduced malaria. Furthermore, to prevent the risk of reintroduction of the disease, the need to strengthen the surveillance of residual anophelism throughout the South should be considered.
Malaria was endemic in Italy until the middle of the last century. Human cases, mainly due to Plasmodium falciparum and P. vivax, were widespread especially along the coastal plains, and before the decisive interventions of reclamation and the launch of the National Anti-malarial Campaign, the disease affected hundreds of people every year [1]. Although Italy was officially declared malaria free by the World Health Organization (WHO) in 1970, since then a few sporadic cases of non-imported malaria have been recorded. Among the most recent cases, four non-travel related malaria cases occurred in Ginosa (Taranto, Apulia region) in October 2017. Integrated entomological surveys were performed, and the presence of the potential malaria vector, Anopheles labranchiae, was recorded in the involved areas [2]. In Italy, there are currently six anopheline sibling species belonging to the Anopheles maculipennis Meigen complex that cannot be distinguished morphologically, including An. atroparvus Van Thiel, 1927, An. labranchiae Falleroni, 1926, An. maculipennis sensu stricto Meigen, 1818, An. melanoon Hackett, 1934, An. messeae Falleroni, 1926, and An. daciae species inquirenda Linton, Nicolescu & Harbach, 2004 [3, 4]. A seventh sibling taxon, Anopheles sacharovi Favre, 1903, once widely distributed throughout the country, progressively disappeared probably because of the progressive modification of its larval habitats [5,6,7,8,9,10]. Among the An. maculipennis complex, An. labranchiae and An. sacharovi were historically considered the two most competent malaria vectors in Italy, always associates with endemic malaria and involved in P. falciparum and P. vivax transmission [11,12,13]. These two species were common and sometimes found in sympatry in Central and South Italy, including the Apulia region [10,11,12,13,14]. Anopheles labranchiae is still abundant and widespread in the region, especially in the Gargano, as recently documented [12, 15]. Contrarily, despite two doubtful findings reported in Northern and Central Italy [16, 17], An. sacharovi has not been found since the last report in the late 1960s. This mosquito thrived in several rural areas, mostly along the north and southwestern coastal plains and in northern Sardinia [5]. Although exophagic activity has been described for this species, it commonly exhibited endophagic and endophilic behaviour, resting in human dwellings, flooded basements and animal shelters where it could bite both day and night [18, 19]. This paper describes the investigation that led to the rediscovery of An. sacharovi in Italy, specifically in the Apulia region.
Even after the anti-malarial campaign following the Second World War, An. labranchiae and An. sacharovi were recorded in Apulia region, often found in sympatry [23]. However due to the diking and draining of marshes and retrodunal ponds, the use of insecticides, urbanization and pollution, many larval habitats, typical of An. sacharovi, have been progressively reduced, and the species was reported in the region until the late 1960s [14]. This heavy anthropic impact has contributed to the rarefaction of An. sacharovi in its distribution, perhaps confining small and limited mosquito populations in restricted natural sites. More recently, a reduction in anthropic pressure, the expansion of natural areas and the creation of new ones, together with other favourable climatic and environmental factors, could have contributed to the slow reconquest of territories and reappearance of the species in Apulia region. The record of Anopheles algeriensis Theobald, 1903, a potential secondary malaria vector, recently reported in Apulia, confirms how these changes can positively allow the Anopheles species to spread and/or recolonize some areas [14, 24]. The recolonization of areas with characteristics favourable to the larval development of An. algeriensis could be a positive signal of environmental requalification, which could also be beneficial for the spread of An. sacharovi. As supported by the literature, An. sacharovi can colonise different types of water collections, such as swamps, marshes, river margins, streams, pools and ditches, and can develop in both freshwater and brackish-salt water collections [18].
Although research projects have often been short and discontinuous, in recent years the collaborative activities conducted by the Experimental Zooprophylactic Institute of Puglia and Basilicata and the Istituto Superiore di Sanit have been able to clearly document the presence of potential malaria vectors, such as An. labranchiae, Anopheles superpictus Grassi, 1899 and An. algeriensis in the Apulia and Basilicata regions [14, 24]. Therefore, after decades of entomological investigations, this notable rediscovery in the coastal areas of southeastern Italy allows us to reintegrate An. sacharovi in the Italian Culicidae fauna. Adults of An. sacharovi were found indoors, either resting in animal shelters or landing on a human during dusk. This highlights not only an endophagic and endophilic behaviour but also a certain degree of anthropophilia of the species. Furthermore, a typical natural breeding site was identified, completing the entomological investigation. Beyond the exceptionality of such findings, it is necessary to underline the importance of strengthening and maintaining constant surveillance of residual anophelism, especially in vulnerable areas where the occurrence of sporadic malaria transmission could be possible. Further investigations will need to assess the distribution and seasonal abundance of An. sacharovi along the southeastern coasts of Italy. However, our findings, confirmed by two point-in-time investigations in 2 consecutive years, represent a valid basis for rethinking and building new models for the prediction and expansion of introduced malaria and for reconsidering the receptivity of the studied areas to malaria to prevent the risk of reintroduction of the disease. Although vector densities do not currently appear to be epidemiologically relevant enough to pose a health threat, the conditions for a renewal of transmission in several Mediterranean countries still exist, as reported in Greece [25], and the occurrence of foci of introduced malaria (in particular by P. vivax) in some regions of our country should not to be underestimated [13].
We are grateful to Inspectors of ASL of Lecce for their help with field surveys and farm contacts and all the breeders, who have always cordially made their stables accessible for the inspections. We also acknowledge the assistance and cooperation provided by the personnel of the Carabinieri Biodiversity Protection Unit of San Cataldo, on duty at the San Cataldo State Nature Reserve, Lecce. Finally, special thanks to Roberto Romi, whose teachings guided and inspired us.
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