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Review

Non-Human Primate Malaria Infections: A Review on the Epidemiology in Malaysia

by
Nor Diyana Dian
1,
Mohd Amirul Fitri A. Rahim
1,
Sherwin Chan
2 and
Zulkarnain Md Idris
1,*
1
Department of Parasitology and Medical Entomology, Faculty of Medicine, Universiti Kebangsaan Malaysia, Kuala Lumpur 56000, Malaysia
2
Department of Microbiology, Tumor and Cell Biology, Karolinska Institutet, 17177 Stockholm, Sweden
*
Author to whom correspondence should be addressed.
Int. J. Environ. Res. Public Health 2022, 19(13), 7888; https://doi.org/10.3390/ijerph19137888
Submission received: 17 May 2022 / Revised: 24 June 2022 / Accepted: 25 June 2022 / Published: 27 June 2022
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Abstract

:
Malaria remains a public health problem in many parts of the world, including Malaysia. Although Malaysia has been recognized as one of the countries free from indigenous human malaria since 2018, the rising trend of zoonotic malaria, particularly Plasmodium knowlesi cases, poses a threat to public health and is of great concern to the country’s healthcare system. We reviewed previously scattered information on zoonotic malaria infections in both Peninsular Malaysia and Malaysian Borneo to determine the epidemiology and distribution of emerging zoonotic malaria infections. Given the high prevalence of zoonotic malaria in Malaysia, efforts should be made to detect zoonotic malaria in humans, mosquito vectors, and natural hosts to ensure the success of the National Malaria Elimination Strategic Plan.

Graphical Abstract

1. Introduction

Malaria remains a public health problem in many parts of the world. It is a life-threatening disease caused by Plasmodium species parasites transmitted to humans through infectious bites of female Anopheles mosquitoes. It can be life-threatening if left untreated, especially among children under five years. In 2019, the World Health Organization (WHO) estimated 229 million malaria cases in 87 endemic countries, significantly reduced by 4% from 238 million cases in 2000 [1]. Despite the decline, approximately 627,000 malaria deaths were still recorded worldwide in 2020, with children under five and service disruptions during the COVID-19 pandemic accounting for 77% and 68% of all malaria deaths, respectively [2]. Malaria is still considered a public health problem in Malaysia and has been on the list of the national notifiable diseases since 1988 [3]. Since the early nineteenth century, it has been recognized as a serious disease in Peninsular Malaysia. It was a significant issue in the Straits Settlements (i.e., a division of British Malaya including Singapore, Penang, Malacca, Labuan, and some smaller islands). Malaria was responsible for one-third of all registered deaths in Penang in 1829 and 40,070 deaths in Peninsular Malaysia in 1944 [4]. The mortality rate due to malaria began to decline after World War II due to numerous antimalarial interventions. Malaria has also long been a problem in Malaysian Borneo (i.e., Sarawak and Sabah), with Sabah recording 250,000 human malaria cases in 1951 [4].
Malaria cases have decreased significantly in Malaysia since the Malaria Eradication Program in Malaysian Borneo and Peninsular Malaysia in 1961 and 1967, respectively [5]. It dramatically reduced malaria cases from 243,870 in 1961 to 4725 in 2012 [6]. Subsequently, the program was strengthened, resulting in zero indigenous human malaria cases (i.e., Plasmodium vivax and Plasmodium falciparum) since 2018 [1]. Despite the significant decrease in human malaria, the emergence of simian malaria is a major public health problem in the less developed areas of Malaysia. In particular, it is a problem among the hard-to-reach indigenous populations (i.e., Orang Asli) in Peninsular Malaysia and the remote interior communities in Malaysian Borneo [3,5,7,8]. In 2019, Malaysia recorded 3222 zoonotic malaria with six fatalities [9]. Furthermore, the influx of migrant workers from malaria-endemic countries and challenges of drug resistance have exacerbated the risk of re-emergence of the disease. Due to the large-scale clearing of forest areas for logging and agricultural purposes, Malaysia faces the problem of increasing cases of simian malaria driven by the migration of macaques to human settlements, particularly in the remote areas where the aboriginal populations live [3,5,8,10]. Although Malaysia has been recognized as one of the countries free from indigenous human malaria since 2018 [1], it is essential to acknowledge the prevalence of non-human malaria and strengthen the effectiveness of the national elimination program.
Given the scattered information on non-human primate Plasmodium parasites in Malaysia, this review is intended to collate previous information on non-human malaria infections in different states of Malaysia (i.e., Peninsular Malaysia and Malaysian Borneo) (Figure 1), including its epidemiology and distribution.

2. Non-Human Primate Malaria Species

In Southeast Asia, at least 11 Plasmodium species infect non-human primates; five of these can be naturally found in macaques, while the remaining mainly infect apes [11]. Infection by these Plasmodium species usually results in very low parasitemia and causes mild or asymptomatic disease in their natural hosts. Since 1960, seven simian malaria species have been reported as transmissible to humans through mosquitoes, i.e., Plasmodium cynomolgi, Plasmodium brasilianum, Plasmodium eylesi, Plasmodium knowlesi, Plasmodium inui, Plasmodium schwetzi, and Plasmodium simium [12]. Three of these are known to pose a potential risk of zoonotic malaria in Southeast Asia. Other than P. knowlesi, which is now known to be the cause of the fifth human malaria [13], two other malaria species capable of infecting humans are P. cynomolgi and P. inui [14,15]. Both of them also share the same natural hosts with P. knowlesi, particularly the long-tailed (Macaca fascicularis) and pig-tailed (Macaca nemestrina) macaques [16].
Simian malaria parasites were first reported in Peninsular Malayan monkeys in 1908 [17]. Initially, it was assumed that simian malaria transmission to humans would not be possible. However, this assumption was dismissed when researchers in the Centers for Disease Control and Prevention laboratories Atlanta, USA, were accidentally infected with a simian malaria species via mosquito bites in the laboratory [15,17]. In 1965, the first natural human infection was reported in an American surveyor in Peninsular Malaysia [18].

3. Plasmodium knowlesi

In the 1930s, P. knowlesi was isolated and thoroughly studied for the first time. Napier and Campbell discovered it in the blood of a long-tailed macaque from Singapore in 1931 while investigating leishmaniasis [19]. They inoculated three macaques, two long-tailed macaques and a rhesus macaque (Macaca mulatta) with the infected blood, and subsequently, the rhesus monkey developed a severe infection [19]. In the following year, the blood form of the P. knowlesi parasite was described by Robert Knowles and his assistant, Das Gupta from the Calcutta School of Tropical Medicine in India. They performed serial-passage of infected blood from the infected monkeys from Napier and Campbell’s study. They also demonstrated the parasite’s ability to infect humans via blood inoculation [20]. In the same year, Colonel John Alexander Sinton, the then Director of the Malaria Survey of India, further investigated the parasite with his coworker Dr Mulligan. They identified specific morphological features of the blood-stage parasite and discovered its unique 24-h schizogonic cycle using the parasite isolated by Knowles and Das Gupta and the parasite they isolated from a long-tailed macaque in Singapore. These findings convinced them that it was a new Plasmodium species [21].
In 1935, Van Rooyen and Pile utilized P. knowlesi to treat patients with neurosyphilis. Patients who were previously infected with P. vivax were less susceptible than those who never had malaria [22]. In the following year, Chopra and Das Gupta successfully treated neurosyphilis in two patients by inoculating them with P. knowlesi from M. fascicularis, thus demonstrating the potential use of P. knowlesi in treating the disease [23]. Until the 1950s, malaria treatment on neurosyphilis patients had been highly effective in Romania. However, the practice was discontinued in 1955 after discovering that the parasite became more virulent after 170 blood transfers and required pharmacological treatment to terminate the infection [23].
The first evidence of P. knowlesi being naturally transmitted to humans was reported in 1965 [18,24]. After spending five days in a primary forest near Bukit Kertau, Pahang in Peninsular Malaysia, an American surveyor acquired the infection. On returning to the United States, he began to experience symptoms and was first diagnosed as being infected with P. falciparum by microscopy. He was then referred to the Army’s Walter Reed Hospital in Washington, D.C., and then to the National Institute of Health’s Clinical Centre in Bethesda, where he was diagnosed with Plasmodium malariae infection. His blood sample was given to a group of malariologists at the National Institutes of Health (NIH) investigating P. malariae and was used to inoculate volunteers at the US Penitentiary in Atlanta, Georgia, who subsequently developed malaria. Rhesus macaques were also inoculated with his blood, resulting in the death of all animals after developing severe illnesses.
Six years later, another human case of P. knowlesi infection was suspected based on presumptive diagnosis six years after the first report of natural human P. knowlesi infection [25]. The diagnosis was based on microscopy and serological tests. From then, no other case of P. knowlesi infection in humans was reported until a large cluster of infections in a community was first detected in the Kapit Division of Sarawak, Malaysian Borneo, in 2004 [24].

4. Plasmodium cynomolgi

Another simian malaria parasite, P. cynomolgi, is also deemed an emerging cause of malaria in humans. The zoonotic capability of P. cynomolgi has been proven through accidental and experimental infections [14,26,27]. Halberstadter and von Prowazek initially found this parasite in the blood samples collected from a cynomolgus monkey [28], commonly known as the crab-eating or long-tailed macaque (M. fascicularis) in Java in 1907. In the rhesus monkey, P. cynomolgi was found to behave similarly to P. vivax, with repeated relapses from an exoerythrocytic source, which later was found to be dormant “hypnozoites” in the liver. It, therefore, became the animal model for relapsing malaria. The potential of P. cynomolgi transmission from mosquito to human was initially demonstrated by the renowned entomologist Don Eyles, who became ill with malaria while studying mosquito transmission in laboratory primates [29,30].
It was previously thought that humans could not be naturally infected with primate malaria parasites. Since then, many artificial human infections have been studied [31,32,33]. P. cynomolgi is similar to P. vivax in morphology, genetics, and biology, albeit having a more extended incubation period of sporozoite-induced infections in humans [31]. P. cynomolgi do not cause severe malaria in experimentally infected individuals. Coatney et al. reported the persistence of initially symptomatic P. cynomolgi human infections for up to 58 days in untreated infections with both the M and B strains [31,32,33]. Like other malaria parasites, persistence in the blood can occur after symptomatic infection, or otherwise, newly acquired infections are almost always asymptomatic, especially if the host has prior exposure. This property can make humans a potential reservoir of the parasite.
P. cynomolgi has been used in several studies on malaria immunity, such as activation of the immune system components during the infection [34,35] and the parasite as a model for malaria-HIV co-infections [36]. The genome of P. cynomolgi encodes orthologues of the vir-gene family, which are responsible for immune evasion in P. vivax [37]. P. cynomolgi has been reported to induce strain-specific immunity, a characteristic seen in both human and rodent malaria parasites [38,39]. The species has also been studied to understand the interactions between Plasmodium and its vector. Furthermore, studies on mechanical characteristics of infections and their genetic basis in mosquitoes [40,41,42], and experiments towards understanding the factors regulating mosquito infectivity, have been conducted [43,44]. P. cynomolgi has also been used to test the efficacy of several new anti-malarial drugs [45,46,47,48,49] and prompted several studies on malaria evolution and genetic diversity [50,51,52].
P. cynomolgi is less restrictive than P. knowlesi in mosquito vector transmissibility [53]. Besides its natural vectors, Anopheles cracens and Anopheles dirus [54,55], it can also be transmitted by Anopheles farauti [56] and by species commonly raised in the laboratory, such as Anopheles gambiae and Anopheles stephensi [57].

5. Plasmodium inui

Besides P. brasilianum, P. inui is the only major non-human primate malaria parasite with a quartan life cycle [14]. While previously assumed to be closely related to P. malariae, recent phylogenetic analyses have included P. inui in the clade of primate malaria parasites that includes P. vivax [58]. Indeed, early immunological findings have suggested its distinction from the P. malariae subgroup [59]. P. inui, originally isolated from a Javan M. fasicularis, may infect a wide range of monkeys, including the New World Platyrrhini [60], and can be transmitted by a range of Anopheles species [61]. This simian malaria parasite has an extended period of development within the vector (i.e., 15 days), it also takes longer to develop during the liver stage (i.e., 9–10 days), as well as adopting a quartan (i.e., 72-h) period of development in the blood [14,60]. Furthermore, P. inui is prone to producing a long-term chronic infection in M. mulatta with blood-stage parasitemia lasting for 14 years or more [62,63]. Although parasitemia is low throughout chronic infections, kidney damage has been documented in animals reminiscent of nephrotic syndrome with chronic glomerulonephritis, which is similarly associated with P. malariae infection [64]. It is important to note that P. inui, especially the OS strain, can cause patent infections in humans [14,31], thus making it a possible zoonotic disease with medical significance [14].

6. Plasmodium coatneyi

P. coatneyi is a tertian malaria species found primarily in macaques in Southeast Asia and is closely related to P. knowlesi [65]. It is transmitted by Asian Anopheline mosquitoes such as A. dirus and Anopheles freeborni, while transmission by A. stephensi and A. gambiae have also been established, although less effective [66]. The evidence for the effective establishment of the erythrocytic cycle in New World monkeys is scarce; however, they appear to be susceptible to the liver stages of the parasite [67]. P. coatneyi liver stages have also been successfully cultured in vitro [68].
P. coatneyi shares some features with the malignant falciparum malaria in humans, i.e., presence of knob protrusions on the surface of infected erythrocytes, cytoadherence to the vascular endothelium, rosetting, and the induction of ‘cerebral malaria’ [69,70,71,72,73,74,75]. P. coatneyi has also been utilized in investigations involving co-infections with schistosomiasis [76] and provides an excellent model for studying the multisystemic dysfunction associated with severe malaria in monkeys [77].

7. Distribution of Knowlesi Malaria Species in Malaysia

In Malaysia, the first naturally acquired P. knowlesi in humans was reported in Pahang in 1965, followed by a second probable case, a few years later in Johor [25]. Both states are located in Peninsular Malaysia. Knowlesi malaria was believed to be a rare disease compared to other malaria species until a large cluster of human infections was discovered in Kapit, Sarawak, in 2004 [24]. Since then, the number of reported knowlesi infections has steadily risen in Sabah and Sarawak, primarily in the interior regions [78,79,80,81,82,83,84,85]. Based on Table 1, most cases of P. knowlesi malaria were detected in the states of Malaysian Borneo (i.e., Sabah and Sarawak).
The geographical topography of Sabah and Sarawak, which have vast forested areas, consist of primary and secondary forests that are habitats for the natural reservoir hosts (i.e., macaques) and the mosquito vector Anopheles. It was found that there is a significant positive correlation between forest density and the number of malaria cases [85]. The density of the forest is important as it increases contact between the human hosts and the habitats of Anopheles mosquitoes, thus increasing the chance for malaria transmission. Zoonotic malaria cases also increased due to the opening of new rubber estates, which necessitate the removal of previously dense forests to construct new roads and new laborers’ villages [85].
Table 1 shows studies conducted in Sabah and Sarawak to determine the prevalence and incidence of knowlesi malaria in the community using molecular PCR technique since it is more sensitive and specific than the standard method for malaria diagnosis [109,110,111,112,113]. PCR proved superior to microscopic examination in detecting human malaria parasites because infected erythrocytes were only commonly observed from blood films with parasitemia above 100,000 parasites/L blood [88,114]. Thus, submicroscopic infections would often give false-negative results. In addition, P. knowlesi parasite shares similar morphological characteristics with P. falciparum in the early trophozoite stage and P. malariae in the later stages of the erythrocytic cycle, which may lead to the misdiagnosis of the causative species [114,115]. A substantial number of P. knowlesi infections have been documented in Sarawak, Malaysian Borneo [24,87,94,98,99,101,102,103,105,114], and in other Southeast Asian countries such as Myanmar [116], Thailand [117,118,119,120,121], the Philippines [122,123,124], and Singapore [125,126,127]. Therefore, P. knowlesi infection in humans is not as uncommon as previously thought, its prevalence is high among the community, and most cases are asymptomatic. Several epidemiological studies conducted in Sarawak had found that P. knowlesi parasite is the main contributor to the total malaria cases (Table 1). It is in line with previously published data that found a high incidence of P. knowlesi malaria in Sarawak [93]. These studies revealed a higher tendency for P. knowlesi than other Plasmodium species among populations in Sarawak. Raja et al. detected 815 (77.8%) P. knowlesi mono-infection cases out of 1047 positive malaria patients from Kapit Hospital, Sarawak, using a molecular method [103], which gives higher sensitivity than the conventional microscopic examination. In addition, several submicroscopic P. knowlesi infections were detected in asymptomatic individuals, as reported by Jiram et al. and Siner et al. [98,101] (Table 1). This is consistent with a study on asymptomatic and/or low-density malaria infection in Malaysia [128]. Accurate diagnosis of asymptomatic submicroscopic malaria is critical in reflecting the actual malaria burden and avoiding ineffective interventions because low levels of parasitemia may serve as a hidden transmission reservoir, thus remaining infectious to susceptible mosquito vectors. The rising incidence of P. knowlesi in Sarawak and the lack of indigenous human malaria cases since 2018 [1] depicts the malaria trend in Malaysian Borneo and Peninsular Malaysia. Furthermore, the highest number of P. knowlesi in Malaysia was contributed mainly from P. knowlesi cases notified in Sabah and Sarawak [105]. The knowlesi malaria occurrence is the highest in Sarawak, possibly due to deforestation and logging activities in some interior regions. Since the forest is a natural habitat for macaques, deforestation displaces macaques to areas near human settlements and increases the risk of parasites transmission from macaques to humans.
In Malaysia, knowlesi malaria cases are not limited to Sabah and Sarawak in the Malaysian Borneo. Cases are also reported in states with dense forest coverage in Peninsular Malaysia, such as Kelantan, Perak, and Pahang [129]. Although epidemiological reports from Peninsular Malaysia were fewer than in Malaysian Borneo, studies showed that P. knowlesi is present in most states in the peninsular (Table 1). As reported by Noordin et al., who conducted a study in four states with the highest incidence rate of malaria in Peninsular Malaysia, 10 out of 19 positive malaria cases were caused by P. knowlesi. In addition, Braima et al. and Vythilingam et al. detected 75 (4.6%) and 65 (58.6%) knowlesi malaria among the communities in Peninsular Malaysia, respectively (Table 1). P. knowlesi and P. malariae can be distinguished with better molecular diagnostic methods. The utilization of molecular diagnostics would better elucidate the extent and coexistence of P. knowlesi in humans, nonhuman primates and vectors.

8. Distribution of cynomolgi, inui and coatneyi Malaria Species in Malaysia

Although 92% of all malaria cases in Malaysia have been due to knowlesi malaria [2], there have also been some cases involving other species of simian malaria. Since 2014, the cases involving simian malaria other than P. knowlesi have been reported to occur naturally in humans. Table 2 shows that P. cynomolgi infection had been recorded in humans in Malaysian Borneo and Peninsular Malaysia. The first case of natural human cynomolgi malaria infection was recorded on the east coast of Peninsular Malaysia (i.e., Hulu Terengganu) in 2014 [12]. Initially, the case was microscopically diagnosed as P. vivax infection but was later confirmed by molecular PCR method as P. cynomolgi. Yap et al. and Grignard et al. reported nine and two mono-infection cases of P. cynomolgi in their studies, respectively [100,108]. As seen in Table 2, P. cynomolgi infection was more commonly reported in humans than P. coatneyi and P. inui. PCR detected these cases among asymptomatic individuals in the communities. It correlates with most studies on human P. cynomolgi infection, which unanimously observed only mild clinical symptoms in infected individuals, if not asymptomatic [29,32,100,103,130]. Due to the limited disease severity and its morphological similarity to P. vivax, accurate microscopic speciation is challenging to make, and the actual incidence rate of P. cynomolgi is likely to be significantly higher than what is currently thought. Indeed, many patients in these studies with P. cynomolgi mono-infection would have been misdiagnosed as P. vivax infections if they had relied only on microscopy or rapid diagnostic test [12,103,130,131,132]. Thus, human infections caused by P. cynomolgi are potentially widely distributed in Malaysia.
P. inui was experimentally reported to infect humans in 1938, with a subsequent report in 1966 [14]. Liew et al. reported two out of 71 cases of asymptomatic P. inui mono-infections in Peninsular Malaysia (Table 2) using nested PCR on concentrated high-volume blood samples. Previously, natural human P. inui infection had not been described [31], even though the parasite is experimentally transmissible to humans [98]. Inui malaria would have been misdiagnosed by microscopy as human malaria parasite since it shares morphological similarities with P. malariae [31,134].
Table 2 shows three coatneyi malaria infections out of 102 Plasmodium genus positive cases reported by Yap et al. [108]. It proved that P. coatneyi infects monkeys and causes natural infection in humans, thus making it a zoonotic disease even though previous attempts at infecting humans using the blood of rhesus monkeys infected with P. coatneyi parasite or via infected mosquitoes were unsuccessful.
The risk of acquiring simian malaria infection is high among the communities living near forest fringes or those who work inside the forest due to the proximity to reservoir hosts and mosquito vectors. High-risk groups include indigenous people, farmers, cultivators, and forest workers [135,136]. Human infection by zoonotic malaria occurs in areas where the vectors and the natural host species co-exist [137]. Local ecological changes, such as deforestation and biodiversity loss, are possible drivers for increased interconnectivity between humans, the reservoir host, and the vector, altering the transmission dynamics of zoonotic malaria infection [97,138]. Understanding the impact and mechanisms of biodiversity loss in an ecosystem on the risk of infectious disease acquisition is a multi-factorial problem [139].
The rapid development of industrial plantations is responsible for mass deforestation in Malaysia, and this trend is expected to continue [140]. It will potentially cause ecosystem imbalance and increase the threat of zoonotic disease outbreaks [141]. The loss of habitat diversity, increasing forest fragmentation, and forest decimation due to deforestation may influence the prevalence of simian malaria parasites and alter the behavior and transmission dynamics between macaques, vectors, and humans [141,142,143].
The social and economic factors that enabled the rapid conversion of forest areas to industrial lands have also been identified [144]. By establishing forest fragments and fringes, the modification of local forested landscapes for anthropogenic use has been proven to provide ideal settings for mosquito populations harboring simian malaria parasites [145,146]. Deforestation impacts the population distribution and density of the macaque host reservoir [97,138], resulting in their invasion into human settlements [142]. Similar to the situation with P. knowlesi, the epidemiology of the P. cynomolgi, P. inui, and P. coetneyi malaria species are significantly affected by forest-clearing activities.

9. Population at Risk

Over the past few years, researchers have been looking at the relationships between environmental, occupational, sociodemographic, and domestic factors that may lead to an increased risk of zoonotic malaria infection, particularly with P. knowlesi. Understanding and identifying these risk variables will aid in the development of appropriate and effective public health interventions for knowlesi malaria. The use of molecular diagnostics has increased the capacity to identify P. knowlesi malaria, and current studies show ongoing environmental and ecological changes affecting its epidemiology. Among the main causes of the increasing number of P. knowlesi malaria cases in Malaysian Borneo include deforestation, reduced biodiversity, and migration of macaques to forest fringes; these developments have increased contact among humans, mosquito vectors, and macaques [84,97,138,143,147,148]. Fornace et al. found that factors such as more than 65% forest coverage within a 2 km radius, more extensive historical forest loss, and lower elevation are associated with increased P. knowlesi infection [97]. They hypothesized that the association could be related to changes in human habitat and changes in the macaque and mosquito environment due to deforestation and agricultural activities. Furthermore, previous studies have also found that farmers, oil palm plantation workers, and people clearing agricultural areas are at high risk of contracting P. knowlesi infection [82,83]. Those living in the habitat of macaques and anopheline vectors of P. knowlesi are also at high risk of infection. Most knowlesi malaria patients in Malaysian Borneo, where most cases have been reported, are adults who work as farmers, hunters, or logging camp workers [24,86]. In Vietnam, it was reported that those at risk live in the forest fringes, collect bamboo and rattan, and work on their farms on the hillsides [149]. Thus, the present high incidence of P. knowlesi infection in Malaysian Borneo can be attributed to its geographical area and the presence of the primary mosquito vectors [150].

10. Mosquito Vectors

The vectors of knowlesi malaria are forest-dwelling mosquitoes that belong to the Anopheles Leucosphyrus group; hence, mosquito population dynamics are an important predictor of malaria risk. As mentioned above, deforestation is one of the significant factors contributing to the increase in the incidence of P. knowlesi infection in Malaysia [135]. However, successful simian malaria transmission can only occur if humans, natural reservoir hosts (i.e., macaques), and competent mosquito vectors are brought into contact. The initial stage in developing control strategies is to identify the vector species responsible for simian malaria transmission and the environments linked with their exposure to humans. The vectors of P. knowlesi malaria in Malaysia comprise five Anopheles species of the Leucosphyrus group, namely, Anopheles hacker, Anopheles latens, Anopheles cracens, Anopheles introlatus, and Anopheles balabacensis [151,152,153,154,155]. These vectors are found mainly in the forests and are outdoor biters. A. balabacensis has been confirmed as the principal vector in the biggest hotspot of human infection in the Kudat district of Sabah [156]. A. latens has been identified as the vector in Kapit, Sarawak, where most human knowlesi malaria cases have been reported. This species prefers to feed on macaques at a higher location and feeds in the forest primarily between 7 and 10 p.m. [152]. It is attracted to both long-tailed macaques and humans [152]. Moreover, a study by Ang et al. found the presence of A. balabacensis and A. donaldi in Lawas, northern Sarawak [157]. Meanwhile, A. cracens is the main malaria vector of the knowlesi parasite in most states in Peninsular Malaysia, with a peak biting time between 8 and 9 p.m. [55]. This species is highly zoophilic and has been found to feed on macaques at the canopy level and humans at the ground level. Land use and land cover change (LULCC) directly impact anopheline mosquito populations, altering the abundance, species composition, and life cycle. Ecological changes in soil, sunshine coverage, types of plantations, water pocket development, and water temperature affect the breeding behaviors of Anopheles malaria vector, with the effects varying among Anopheles species [158]. Deforestation reduces shaded water bodies, the preferred breeding ground for some Anopheles species. Other Anopheles species thrive in water bodies with more sunlight which can increase larval survival, adult productivity, and intrinsic growth rates and shorten the gonotrophic cycles to increase the vectorial capacity [159]. Furthermore, environmental and climatic changes caused by LULCC may favor the survival of several Anopheles species, permitting long-term malaria transmission or affecting the availability of hosts and blood meals [158]. Temperature rises and changes in rainfall patterns may result in a more extended malaria season in many sub-Saharan African regions and affect the local vectorial capacity [160]. Thus, climate changes affect the transmission dynamics of simian malaria, influencing the parasite density in humans, mosquito vectors, and natural reservoir hosts.

11. Reservoir Hosts

Humans can acquire knowlesi malaria when the habitats of humans, macaques, and competent mosquito vectors overlap, mainly due to various human activities that destroy the natural forest ecosystem. Subsequently it can lead to an increase in the incidence of zoonotic malaria in Malaysia. Long-tailed (M. fascicularis) and pig-tailed (M. nemestrina) macaques from Singapore [20] and Peninsular Malaysia [55] have been identified as reservoir hosts of P. knowlesi. Macaque populations tend to wander around village areas (average distance of 6 km), and areas inside the forest with lower elevation and warmer temperatures [137]. A single P. knowlesi infection from a leaf monkey (Presbytis melalophos) from Peninsular Malaysia [161] has also been reported. The presence of monkeys in peri-domestic areas is a substantial predictor of risk, indicating that monkey to human transmission is still the most common mode of transmission, rather than human to human transmission.

12. Discussion

Although Malaysia has successfully eliminated indigenous human malaria species [1,3,7,8], P. knowlesi malaria continues to infect many people in the country’s rural areas [84,92,99]. In Sarawak (Malaysian Borneo), zoonotic malaria caused by P. knowlesi infections was studied extensively from 2004 [24] and was eventually found to be a common cause of malaria [162,163]. Besides P. knowlesi, increasing evidence of naturally acquired cynomolgi infection in humans was also documented in Malaysia [132], highlighting the risk of zoonotic malaria infections in the country.
Successful transmission can only occur if the competent vectors and the natural hosts co-exist in proximity, leading to a rising number of zoonotic malaria cases. Humans and macaques can share the same habitat, particularly those who practice agriculture or farming near the forests or visitors who encounter macaques in their natural habitat. The availability of appropriate vectors and the close contact and geographical distribution between humans and macaques can lead to malarial disease transmission between the two populations [137,164,165]. Zoonotic malaria infection in humans is influenced by many factors, including anthropogenic LULCC that inadvertently alters the transmission dynamics among the macaque reservoirs, the vectors, and the people, as seen in Malaysian Borneo [158,166]. Macaques, who have lost their natural habitats due to deforestation for palm oil plantations or other clearing activities, are then coerced to encroach on human settlements resulting in a rise in the prevalence of zoonotic malaria infection in humans [83].
It is vital to address zoonotic malaria as one of the threats to public health problems in Malaysia. Zoonotic malaria cases are widely reported in Malaysian Borneo, as concluded by many studies [7]. In Peninsular Malaysia, only 13 epidemiological studies have been performed over the past 40 years, most of which have still relied on conventional microscopy [7]. This could lead to an underrepresentation of the actual incidence of zoonotic malaria in the community. Further studies and continued surveillance of zoonotic malaria parasites in Malaysia are necessary, using sensitive molecular methods to obtain accurate and reliable data for monitoring these emerging zoonotic infections.

13. Conclusions

In conclusion, zoonotic malaria constitutes a public health concern in Malaysia and other Southeast Asian countries. The natural habitats of the hosts and vectors and the evolution of the parasite could drive the transmission of this neglected but emerging disease. Moreover, the global environmental and climate changes could affect the dynamics of transmission of simian malaria as an emerging human cause of malaria. Further studies using molecular and multi-disciplinary approaches to detect simian malaria infection in humans, vectors, and natural hosts are necessary to ensure the success of the National Malaria Elimination Strategic Plan in Malaysia.

Author Contributions

Z.M.I. and S.C. conceived and designed the study; N.D.D., M.A.F.A.R. and Z.M.I. acquired, analyzed, and interpreted data; N.D.D. drafted the manuscript; Z.M.I. and S.C. provided critical revisions. All authors have read and agreed to the published version of the manuscript.

Funding

This work was supported by the SEAOHUN Small Grant Program with the generous support of the American people through the US Agency for International Development (USAID) One Health Workforce-Next Generation (OHW-NG) Award 7200AA19CA00018 (Grant number: FF-2021-457), the ASEAN Science, Technology and Innovation Fund (Grant number: FF-2019-124), and the Faculty of Medicine, Universiti Kebangsaan Malaysia (Grant numbers: FF-2019-124/1 and FF-2021-350). The contents and associated materials are the responsibility of the authors and do not necessarily reflect the view of USAID or the US Government. The funder had no role in the study design, data collection and interpretation, or the decision to submit the work for publication.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Acknowledgments

We sincerely thank Rahmah Noordin for critical reading of the manuscript.

Conflicts of Interest

The authors declare no conflict of interest.

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Ijerph 19 07888 g001 550
Figure 1. Map of Malaysia showing all states and federal territories.
Figure 1. Map of Malaysia showing all states and federal territories.
Ijerph 19 07888 g001
Table
Table 1. Distribution of P. knowlesi parasite reported in Malaysia.
Table 1. Distribution of P. knowlesi parasite reported in Malaysia.
Publication YearStudy Area (States) in MalaysiaSampling YearStudy
Design		No. of Blood Samples TestedNo. Positive Plasmodium spp.Incidence or Prevalence of P. knowlesi (%)References
2004Sarawak2000–2002Prospective208208106 (51)[24]
2008Perlis, Kedah, Pulau Pinang, Perak, Kelantan, Terengganu, Pahang, Selangor, Melaka, Negeri Sembilan, Johor, Kuala Lumpur2005–2008Prospective11111165 (59)[55]
2008Sabah, Sarawak, Pahang2001–2006Prospective10141014280 (28)[86]
2009Sarawak2006–2008Prospective169169107 (63)[87]
2009Sarawak1996Retrospective473629 (62)[88]
2011Sabah2010Retrospective24310763 (26)[78]
2011Sabah2007–2009Prospective787856 (72)[89]
2012Sabah2009–2011Retrospective18,993445339 (2)[85]
2013Selangor2006–2012Prospective1623162375 (5)[90] *
2013Sabah2008–2011Prospective18918942 (22)[91]
2013Sabah1992–2011Prospective1461814,6182181 (15)[92]
2013Sabah2010–2011Retrospective387295130 (34)[79]
2014Sabah2010–2013Retrospective13661082924 (68)[80]
2014Sabah, Sarawak, Perlis, Kedah, Pulau Pinang, Perak, Kelantan, Terengganu, Pahang, Selangor, Melaka, Negeri Sembilan, Johor, Kuala Lumpur2012–2013Retrospective457453256 (56)[93]
2014Sarawak2010–2011Prospective404028 (70)[94]
2015Sabah2012–2013Prospective207207152 (73)[95]
2016Sabah2012–2013Retrospective12910967 (52)[96]
2016Sabah2012–2014Retrospective114720620 (2)[97]
2017Sarawak2014–2015Cross-sectional300287 (0.3)[98]
2017Sarawak1992–2014Prospective936493649364 (100)[99]
2019Sabah2015Cross-sectional876543 (0.3)[100]
2019Sarawak2013–2014Cross-sectional2511189 (4)[101]
2020Sabah, Sarawak, Perlis, Kedah, Pulau Pinang, Perak, Kelantan, Terengganu, Pahang, Selangor, Melaka, Negeri Sembilan, Johor, Kuala Lumpur2000–2018Prospective117,224117,22419,975 (17)[102]
2020Sarawak2013–2017Prospective10471047815 (78)[103]
2020Johor, Pahang, Kelantan, Selangor2019–2020Cross-sectional5851910 (2)[104]
2020Sabah, Sarawak, Perlis, Kedah, Pulau Pinang, Perak, Kelantan, Terengganu, Pahang, Selangor, Melaka, Negeri Sembilan, Johor, Kuala Lumpur2013–2017Prospective16,50016,50011,380 (69)[105]
2020Sabah2015–2017Prospective386738673524 (91)[84]
2020Sabah2016Cross-sectional1222410340 (28)[106] *
2021Sabah, Sarawak, Kuala Lumpur, Perak, Pahang, Pulau Pinang, Terengganu2015–2016Retrospective1128054 (48)[107]
2021Sarawak, Pahang, Perak, Selangor, Negeri Sembilan, Melaka, Kelantan2011–2014Retrospective64510240 (6)[108]
* Cases detected only by microscopy examination with no PCR performed.
Table
Table 2. Published studies of P. cynomolgi, P. inui, and P. coatneyi in Malaysia.
Table 2. Published studies of P. cynomolgi, P. inui, and P. coatneyi in Malaysia.
Publication YearStudy Area (i.e., State in Malaysia)Sampling YearStudy DesignNo. of Blood Samples TestedNo. of Positive Plasmodium spp.No. of Simian Malaria Species, (n)References
2014Terengganu2011Case report11P. cynomolgi[12]
2019Terengganu2018Case report11P. cynomolgi[131]
2019Sabah2015Cross-sectional87654P. cynomolgi (2)[100]
2020Sarawak2013–2017Prospective10471047P. cynomolgi (6)[103]
2021Pahang, Perak, Selangor, Negeri Sembilan, Melaka, Kelantan, Sarawak2011–2014Retrospective645102P. cynomolgi (9), P. coatneyi (3), and P. inui (3)[108]
2021Pahang2020Cross-sectional712P. inui (2)[133]
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Dian, N.D.; Rahim, M.A.F.A.; Chan, S.; Idris, Z.M. Non-Human Primate Malaria Infections: A Review on the Epidemiology in Malaysia. Int. J. Environ. Res. Public Health 2022, 19, 7888. https://doi.org/10.3390/ijerph19137888

AMA Style

Dian ND, Rahim MAFA, Chan S, Idris ZM. Non-Human Primate Malaria Infections: A Review on the Epidemiology in Malaysia. International Journal of Environmental Research and Public Health. 2022; 19(13):7888. https://doi.org/10.3390/ijerph19137888

Chicago/Turabian Style

Dian, Nor Diyana, Mohd Amirul Fitri A. Rahim, Sherwin Chan, and Zulkarnain Md Idris. 2022. "Non-Human Primate Malaria Infections: A Review on the Epidemiology in Malaysia" International Journal of Environmental Research and Public Health 19, no. 13: 7888. https://doi.org/10.3390/ijerph19137888

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