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Zoonotic parasites associated with predation by dogs and cats
Parasites & Vectors volume 16, Article number: 55 (2023)
Abstract
One of the most common behaviors of cats that have an indoor/outdoor lifestyle is to bring hunted “gifts” to their owners, represented by small mammals, reptiles and birds. Access to the outdoors by dogs and cats may represent a problematic issue, since they may be at risk of diseases, traffic accidents and ingestion of toxins. Yet, the impact of this population of roaming dogs and cats predating wildlife is another concerning issue that receives less attention. Despite these risks, most owners still prefer to give outdoor access to their pets to allow them to express their “natural instincts,” such as hunting. Therefore, with a growing population of > 470 million dogs and 373 million cats worldwide, predation not only represents a threat to wildlife, but also a door of transmission for parasitic diseases, some of them of zoonotic concern. In this review, the role played by dogs, and especially cats, in the perpetuation of the biological life cycle of zoonotic parasites through the predation of rodents, reptiles and birds is discussed. Feral and domestics dogs and cats have contributed to the population collapse or extinction of > 63 species of reptiles, mammals and birds. Although the ecological impact of predation on wild populations is well documented, the zoonotic risk of transmission of parasitic diseases has not received significant attention. The parasitic diseases associated to predation vary from protozoan agents, such as toxoplasmosis, to cestodes like sparganosis and even nematodes such as toxocariasis. Raising awareness about predation as a risk of zoonotic parasitic infections in dogs and cats will aid to create responsible ownership and proper actions for controlling feral and free-roaming cat and dog populations worldwide.
Graphical Abstract
Background
To a cat owner, waking up in the morning or arriving home after an exhausting day at work just to find that “Milo” is playing in bed or near the kitchen with a half-dead lizard is an unpleasant event that may not be so uncommon as many would like it to be. Indeed, cats are known to not just hunt small reptiles, rodents and birds, but also to bring to their owners some of the day's hunt as a “gift” [1, 2]. In fact, dogs, but especially cats, represent top predators that can adapt to virtually any type of environment, mostly near urban settlements, as well as feral populations of dogs and cats that continue to be on the rise in all continents [3, 4]. Domestic dogs and cats have been part of our society for > 10,000 years [5,6,7]. An emotional attachment to these species is evident in most of the western world and has created a more permissive culture toward behaviors that may have consequences in conservation and animal welfare, such as allowing animals to have unrestricted access to the outdoors [8, 9]. These behaviors are more evident in cats who are allowed to wander and have a partial to total outdoor life [10]. This lifestyle is debatable, and even today there is no consensus on whether cats should be allowed to go outside or not [11,12,13]. However, the devastating consequences of feral populations and outdoor dogs and cats produce in the decline of the native fauna is not debatable [14, 15]. Indeed, recent studies have shown the direct and high impact of predation by dogs and cats on populations of small mammals, birds, reptiles and amphibians [16,17,18]. Thus, it has been consistently advocated to avoid outdoor lifestyles and to reduce the feral dog and cat populations to decrease their impact on the native fauna as well as to avoid the further extinction of wild species [19,20,21]. Conversely, other problematics raised by predation have been scarcely discussed [22]. Indeed, predation is one of the most efficient strategies of parasite transmission, as it is a direct way for a parasite to complete its life cycle, depending on the trophic chain [23, 24]. Trophic-transmitted parasites have, in many cases, evolved strategies to enhance predation via prey manipulation [25]. For example, Toxoplasma gondii (Eucoccidiorida: Sarcocystidae) depends on the ability of feline predators to feed on small rodents and other prey species to complete its life cycle [26, 27]. Hence, one of the diseases that has been used as a paradigmatic example to avoid the predatory behavior of cats and dogs is toxoplasmosis, which is a highly prevalent parasite in cat and human populations [28, 29]. Therefore, in this review we discuss the parasitic diseases associated with predation, with a focus on those that are of zoonotic concern, to further evidence the risk of transmission of parasitic diseases associated to outdoor lifestyle of dogs and cats.
Greta and Valma are top predators: origin of domestic feline and canine populations
The domestication process of dogs and cats was quite different and ultimately resulted in a diverse range of breeds, sizes and phenotypes of dogs but a more conserved and almost ancestral form of modern cats [30,31,32,33]. On one hand, the domestication of dogs occurred around 10,000 years ago, based on a need of primitive humans to hunt in packs, as wolves do [34, 35]. Thus, modern dogs originated from wolves, using empiric knowledge and soon after that of genetics to create breeds with different purposes (e.g. hunting, searching, company) [35]. On the other hand, domestication of modern cats is believed to had happen several thousands of years before the domestication of dogs [36, 37]. The relationship between cats and humans had a pest control purpose, aiding human populations in keeping the rodent and other vermin populations under control, eventually favoring the transformation of a hunting-based society to a farming, stable human population. Given this unique purpose of cats, besides being company to their owners, breeds of cats were created solely with an esthetic purpose, with more than 50 modern breeds of cats [38]. Despite this relatively large number of cat breeds, the modern cat morphology has not changed as dramatically as that of dogs. Furthermore, cats and hunting breeds of dogs still maintain their predatory instincts.
Dogs and cats are a pivotal part of modern civilization, as more than half of the human global population is estimated to have a pet at home, dogs being the most popular, present in one of three homes worldwide [39, 40]. In addition, almost a quarter of pet owners have a cat [41]. For example, in a survey conducted in 2021–2022 in the USA, about 70% households (i.e. 90.5 million families) owned a pet, specifically 45.3 million cats and 69 million dogs, with a total pet industry expenditure of $123.6 billion [42, 43]. Apart from the growing domestic dog and cat population (estimated around 900 million and 600 million, respectively), a large portion of this number is represented by wild and feral animals, which make up to more than half of the total number [21, 44]. In addition, feral populations have a major negative impact on conservation and disease transmission [21]. Specifically, the dog and cat population can be classified in three main groups (Fig. 1): domesticated or companion animals, which are animals that are in tight contact with humans, receive proper husbandry and healthcare, have a lower burden of parasites and predate occasionally on small animals [45]. Stray animals are those that have occasional contact with humans. Thus, some of them receive less food and shelter, as well as healthcare, being more exposed to parasites and feeding mainly on small prey [46, 47]; feral animals are those that have no contact with humans and are independent. Thus, they do not receive food or healthcare, have a higher burden of parasites and feed mainly on small prey [48]. There is a large and ongoing debate on control policies for these “wilder” populations of dogs and cats [49, 50]. Regardless of this classification, cats have a more independent nature than dogs, which makes them more prone to hunt than stray or domesticated dogs. Moreover, dogs in general can be trained to reduce their hunting behavior, differently from cats, which have a very strong hunting instinct, which often is even encouraged by owners [51].
Given humanity’s emotional attachment to cats and dogs, the general appeal and tight relationship between dogs, cats and humans has hindered their population control, since reduction or elimination plans may be considered animal abuse [52,53,54]. Hence, policy makers and legislators have imposed softer control measures such as the Trap-Neuter-Return (TNR) program in the USA for cats or the outdoor cat colonies in many countries in Europe, completely prohibiting euthanasia as a control measure [55, 56]. Consequently, invasive cat and dog populations have had a devastating impact in places such as Galapagos Islands, Mauritius, Madagascar and Australia, to name a few [57,58,59,60].
Predation and its impact beyond conservation
Dogs and cats, especially those with feral behavior, represent an important threat to biodiversity. However, predation also may be a gateway for the transmission of parasites, some of which may have zoonotic potential, threatening not only our companion animals but also human health [61, 62]. Despite this potential of zoonotic transmission, most efforts and studies have been focused on the impact of predation in conservation [63,64,65,66]. Indeed, many studies have correlated the presence of dogs and mainly cats with the decline or extinction of native populations. For example, cats were the partial cause of the extinction of the Stephens Island wren (Traversia lyalli) in New Zealand [67]. Likewise, cats have reduced the native fauna in many ecosystems and caused the extinction of small animals on islands [68,69,70]. The primary trophic source for dogs and cats is small mammals, birds, reptiles and invertebrates [71, 72]. Although feral populations contribute mainly to the predatory pressure on small prey, domestic dogs and cats with an outdoor lifestyle also have an important impact on endemic populations of wildlife, being also a source of zoonotic infection for human beings. For example, studies in suburban areas of the US demonstrated that > 44% of cats that had outdoor lifestyles preyed on small wild animals, with 23% of their prey being brought back to their owners [73]. Considering this, prey brought back to the household may represent another transmission route of parasites (Fig. 2), apart from fecal-oral transmission, more important than currently acknowledged [74].
The deleterious impact of predation has been particularly evident on islands such as in Australia and New Zealand, where no other predators were present; thus, the wildlife was more vulnerable to invasive predators, such as dogs and cats [75, 76]. Indeed, it is estimated that feral cats kill > 466 million reptiles per year in Australia, where a single cat may kill up to 225 reptiles per year [76]. However, the situation is not less worrisome elsewhere. Studies estimated that > 478 million reptiles are killed by cats in the US per year [16]. Conversely, the impact of dog predation has been less assessed and quantified. However, studies performed in Tasmania, showed that dogs also are a cause of native wildlife population decline and disturbance [77]. Dogs may also have a devastating effect on small and vulnerable populations, such as the complete annihilation of the largest flamingo colony in Sardinia, Italy [78] or the predation of 55.5% (500/900) of a kiwi bird population by a single dog in New Zealand [79]. Overall, dogs and cats are estimated to have caused the extinction of > 63 species of small animals (i.e. rodents, birds, reptiles and amphibians) (Fig. 3) [68]. However, of all the invasive species (e.g. red foxes, pigs, dogs, mongoose, wild boars), cats are the primary cause of population decline and extinction of endemic animals worldwide [80]. Therefore, though feral and colony cats are the main threat to vulnerable endemic species, especially on islands [57, 61, 64], their control and eradication are under debate because of the perception of “beneficial” predation of cats toward pest populations of mice and rats [81].
Overall, predation is a typical ancestral behavior of dogs and cats, which greatly affects many ecological processes, ultimately favoring parasites in the completion of their biological life cycle. Indeed, parasites not only regulate ecological processes, reducing host survival and fitness [82, 83], but also host abundance [84]. Nonetheless predation has long been overlooked in many fields of parasitology, such as parasite ecology, biology and epidemiology [85], resulting in lack of knowledge on the role prey may exert on the maintenance and control of parasitic diseases of dogs and cats. This is also due to the difficulties in studying intermediate and paratenic hosts in parasitology, which are mainly related to the long time required for running those studies under field conditions. Nevertheless, in this review we highlight and point out some parasites of zoonotic concern that are strictly related to predation as a strategy to complete their life cycle.
Predation and zoonotic parasites
Many species of parasites (i.e. genera Spirura, Physaloptera, Gnathostoma, Diplopylidium or Joyeuxiella) use small animals, such as rodents, reptiles and birds, as intermediate or paratenic hosts and dogs and cats as definitive hosts. While most of these parasites are specific for their animal hosts, other are of zoonotic concern (Table 1) [62, 86, 87]. Recent extrinsic factors (e.g. environmental and climate modifications, urbanization, habitat fragmentation) have favored the trophic transmission of parasites [88, 89]. This has resulted in an increased risk of spill-over of parasites from wild to peri-urban and urban settings favoring the contact of predators and prey, along with the parasites they carry. For example, in Australia two zoonotic parasitic diseases associated with the presence of cats are toxoplasmosis and sparganosis, carried by Spirometra spp. (Cestoda: Diphyllobothriidae), which may overtly spill over to native fauna and human populations [90]. Indeed, toxoplasmosis, besides being of great public health concern, has contributed to the decline of native mammal and bird populations, such as the urban populations of the Eastern Barred Bandicoot (Perameles gunnii) [91]. The other disease highly prevalent in feral cats in Australia is sparganosis, which causes human infection and also affects native fauna [92].
The presence of cats and dogs is also associated with gastrointestinal parasites that can be of medical and veterinary importance. Furthermore, these animals can have an important role as spreaders of these parasites through fecal contamination of soil, vegetables and water (Fig. 2). Studies assessing the prevalence of zoonotic gastrointestinal parasites in the feces of stray dogs and cats have constantly pointed out the high number of infected animals with a myriad of parasites pathogenic to humans [46, 48, 93]. This high prevalence is mainly related to the absence of preventative or deworming protocols in feral populations of dogs and cats as well as the availability of infected prey. In addition, most owners are not aware of the possibility of zoonotic parasites from their dogs and cats [40]. Moreover, free-roaming, feral, colonies or house cats with outdoor access, as well as dogs with the same outdoor lifestyle, may defecate in public spaces, increasing the likeability of human exposure [94]. Companion dogs and cats that are allowed to defecate in public places, where feces are not collected or disposed of properly, also represent an important source of environmental contamination [95]. To highlight the impact of dog and cat populations with outdoor lifestyle on the trophic transmission of zoonotic parasitic diseases, examples of the main groups of parasites are given below.
Not only Toxoplasma: zoonotic protozoa that are transmitted by predation
For its pathogenicity during gestation in many animal species, including humans, toxoplasmosis by T. gondii [96] is probably one of the most important and better known zoonotic protozoan infections. A wide range of warm-blooded animals are intermediate hosts of this protozoan, while felids are definitive hosts. The biological life cycle in cats is typically perpetuated by their predation of rodents, such as mice (Fig. 3a). For example, in a cat population in southern Poland 68.8% of animals were serologically positive for T. gondii with a significantly greater prevalence in older (> 1 year) (83.5%) than in younger cats (48.3%) and in cats kept outdoors than indoors (69.7% vs. 16.7%) [97]. The occurrence of T. gondii infection in marine mammals has raised concerns about the role reptiles (e.g. turtles, crocodiles, snakes), amphibians (e.g. frogs, toads) and fish may play as a source of infection [98]. Of the 2988 samples of cold-blooded animals examined in 26 studies reviewed in the literature [98], the number of positive cases of T. gondii (n = 129) was not sufficient to assess the real involvement of these animal species in the biological life cycle of this protozoan.
Other less studied protozoan diseases are represented by other coccidia (Table 1), for example acute muscular sarcocystosis caused by Sarcocystis nesbitti (Eucoccidiorida: Sarcocystidae) [99]. This species of Sarcocystis, initially detected in southeast Asia (Malaysia), produces a muscular presentation after the ingestion of sporocysts in food (e.g. uncooked snake meat) or water contaminated with feces from infected definitive hosts (i.e. cats, snakes, humans). This disease has produced a number of recent outbreaks, with > 100 human patients suffering from acute muscular illness on Tioman Island, Malasyia [100], and 89 human patients with molecularly confirmed symptomatic muscular sarcocystosis on Pangkor Island [99]. Most of the cases are associated with the consumption of untreated water [101].
Moreover, the presence of feral cats greatly impacts human and livestock health costs associated with protozoan zoonotic diseases (i.e. toxoplasmosis and human and livestock sarcocystosis) [102]. In Australia, the human costs of these diseases are estimated to be > $6.06 billion Australian dollars per year, and the costs of toxoplasmosis and sarcocystosis affecting sheep and cattle, respectively, are > $11.7 million Australian dollars [102]. Health costs in humans are associated with cats being the definitive hosts of the toxoplasmosis causative agent, thus affecting human health via congenital disease, symptomatic toxoplasmosis and mental health issues.
Dogs and cats may have a role in spreading protozoan species that are associated with environmental contamination, such as Cryptosporidium (Eucoccidiorida: Cryptosporidiidae), which causes diarrhea in humans, often leading to outbreaks [103]. Cryptosporidium parvum global prevalence in dogs (i.e. 1.28%) [104] was most related to dogs with outdoor lifestyles (i.e. kennel, shelter or stray dogs), which are highly exposed (e.g. 5% in kennel dogs and 1.5% in privately owned dogs from Italy [105]). However, Cryptosporidium is globally more prevalent in cats (i.e. 6%) and has a higher prevalence in rural areas and in cats with outdoor lifestyle, associated with livestock and wild animals [106]. Dogs and cats may become infected with zoonotic genotypes of C. parvum through fecal-oral transmission or, in some cases, ingesting infected prey [107]. Besides the host-specific Cryptosporidium felis, other species have been detected in cats, such as rodent-associated Cryptosporidium muris and Cryptosporidium rat genotype II, III and IV [108]. However, infection with rodent-associated Cryptosporidium spp. in cats may be the result of mechanical transmission due to predation of infected rodents [109]. Hence, future studies to assess the role of predation in the zoonotic transmission and circulation of pathogenic protozoa by dogs and cats are needed.
Tapeworms in prey: cestode diseases associated to predation
Four genera of Cyclophyllidea cestods (Bertiella, Dipylidium, Raillietina and Mesocestoides) are potentially zoonotic, though less studied and often reported as uncommon findings [110]. In particular, Dipylidium, Mesocestoides and Raillietina, associated with carnivores and rodents, respectively [111], can also have reptiles implicated in their biological life cycles. Indeed, through predation of secondary intermediate hosts (e.g. birds, reptiles and amphibians; Fig. 3b–d), dogs and cats may be infected by Mesocestoides lineatus and Mesocestoides literatus (Cyclophyllidea: Mesocestoididae), which usually proliferate in their peritoneal cavity as undifferentiated larval stage causing ascites. While adults of these parasites are present in the intestine of carnivores, larval stages perpetuate in two intermediate hosts. The first is probably represented by arthropods (with cysticercoid larvae) and the second by insectivorous vertebrates, harboring elongated larval tetrathyridia (Fig. 4a, b). The identity of the intermediate hosts and biological life cycle remain enigmatic, terrestrial arthropods (e.g. dung beetles, ants, roaches and mites) being considered first intermediate hosts, with the development of metacestode stage following the ingestion of proglottids/oncospheres with the feces of the definitive hosts [112]. Furthermore, the detection of pre-tetrathyridial stages in the body cavity of a ground skink (Scincella lateralis) further complicated the understanding of the biology of Mesocestoides spp., suggesting that tetrathyridia could develop from hexacanth embryo within a single vertebrate host [113]. Mesocestoidosis is sporadically found in dogs and cats that hunt, typically in rural environments. Human cases of infections have been attributed to M. lineatus in Asia and Mesocestoides variabilis in North America, though the species identification mainly relies on the geographic origin of these cestodes rather than a clear morphological and/or molecular delineation [110, 114]. In addition, the plasticity of the morphology of larval forms and proglottids and the poor conditions of samples referred by patients hamper a clear understanding of the zoonotic infection routes. Of the 27 human cases of intestinal infections reported by Sapp and Bradbury [110], half are from East Asia (Japan, Korea and China) and the rest from the USA, with one from Rwanda; all were classified as foodborne infections due to the consumption of tetrathyridia in undercooked meat and organs of snakes [110]. Cases from North America, mainly in young children, suggest that these may occur through contact with a variety of exotic pets and geophagy, though these are unlikely a source of tetrathyridia ingestion. In addition, the ingestion of an arthropod first intermediate host (yet unknown) should imply the development of tetrathyridia but not an adult intestinal infection. However, considering that tetrathyridial infections have been documented in non-human primates [115,116,117], and that in carnivores it is mainly diagnosed in animals during abdominal surgery or necropsy, the absence of cases in humans could be due to the low number of diagnostic opportunities compared to finding scolexes in the patients’ feces. All the above render knowledge about the routes of zoonotic infections and their diagnosis quite complex and enigmatic.
Furthermore, taeniid cestodes may also be associated with predation as their larval stages depend on an intermediate host (Fig. 4c) [118]. One of the most life-threatening cestode diseases is represented by echinococcosis, with Echinococcus multilocularis (Cyclophyllidea: Taeniidae) being strictly associated with predation of small rodents (e.g. voles) by foxes and dogs [119]. Adult cestodes develop on the intestine of canids, which excrete infective eggs in feces that are ingested by intermediate hosts. Humans are infected once in contact with a contaminated environment or eggs adhered to dog fur, causing alveolar echinococcosis (Fig. 5) [120]. This disease is prevalent in the northern hemisphere (e.g. central Europe, the USA, Japan), becoming increasingly present in urban settings [119, 121]. For example, in Switzerland, E. multilocularis is present in urban areas (i.e. the city of Zurich) because of increasingly synanthropic foxes, serving as definitive hosts, that feed on rodents. In the urban or rural context, free-roaming dogs and cats can become infected by preying on rodents (Fig. 5) [119, 122]. Hence, infected cat and dog populations represent an important zoonotic risk [123]. Indeed, in areas of China where there are large populations of dogs and cats, the risk of infection is higher than that associated with the activity of fox hunting [124].
Other taeniid cestodes associated with lagomorphs and rodents as intermediate hosts, and dogs and cats as definitive hosts, are Taenia serialis and Taenia brauni (Cyclophyllidea: Taeniidae) [125, 126], which are prevalent in hunting and stray dogs and in cats, in rural areas [126]. Usually, humans become infected after ingesting eggs from the environment, causing subcutaneous or ocular coenurosis, as reported in many cases in Africa [127, 128].
Another group of medical and veterinary important cestodes are the water-associated tapeworms of the genus Spirometra (Pseudophyllidea: Diphyllobothriidae), which use dogs, cats and other carnivores as definitive hosts. The most common species found in dogs is Spirometra mansoni, and in cats Spirometra erinaceieuropaei [129]. Intermediate hosts are represented by aquatic crustaceans (first intermediate hosts, harboring procercoids) and aquatic or semi-aquatic vertebrates, such a fish, amphibians and reptiles (second intermediate hosts, harboring plerocercoids). Both procercoids and plerocercoids (also known as spargana) are infective to humans through ingestion of contaminated water, contact or consumption of second intermediate hosts [130, 131]. Sparganosis is frequently reported in Southeast Asia because of common consumption of raw or uncooked snake and frog meat; however, the disease is also present in Africa, the Americas and Australia [128]. A meta-analysis review estimated the global prevalence of Spirometra in dogs to be 0.0723%, with S. mansoni being the most prevalent species (0.141%) in low-income countries (0.288%) of Africa (0.224%). In the same study, cats presented a higher prevalence (0.1040%), with S. erinaceieuropaei as the most prevalent species (0.268%) in lower-middle income countries (0.134%) of Oceania (0.203%) [129, 132].
Zoonotic nematodes of dogs and cat associated with predation
Many nematodes take advantage of the predator-prey relationship, such as metastrongylids, which use gastropods (i.e. snails and slugs) as intermediate hosts, and a myriad of small animals (i.e. rodents, birds, snakes, lizards) as paratenic hosts (Fig. 4d) [133]. Most of these species (e.g. Aelurostrongylus abstrusus, Troglostrongylus brevior in cats and Angiostrongylus vasorum in dogs) affect only their definitive hosts and have no zoonotic risk [134, 135]. However, zoonotic nematodes of the order Ascaridida (i.e. Toxocara) and Strongylida (i.e. Ancylostoma, Uncinaria) are also associated with the predator-prey relationship, in this case using prey as paratenic hosts [86, 136]. Predation of rodents and birds is important for the completion and maintenance of Toxocara canis and Toxocara cati (Ascaridida: Toxocaridae), which are worldwide distributed parasites of dogs and foxes, and of cats and other felids, respectively. Toxocariases are regarded as neglected tropical diseases with an overall seroprevalence in the human population of up to 16% [137] and a global population of positive dogs as high as 40% and cats up to 76% [138]. While the infection mainly occurs through the ingestion of larvated eggs from the environment, the predation of paratenic hosts carrying somatic (hypobiotic) L3 represents a major component in the maintenance and perpetuation of the biological life cycles of these zoonotic helminths [139,140,141]. Though ascarid larvae do not develop in the paratenic hosts, they may survive for up to 10 years, continuing the parasite life cycle for prolonged periods if the paratenic host is consumed by the definitive one [139, 142]. Following the ingestion of larvated eggs by paratenic hosts, larval migration can cause clinical disease (larva migrans) depending on the number of larvae and on the organs infected. Paratenic hosts (rodents or birds) harbor larvae in the liver, skeletal muscles or brain tissue, according to host species, with potential consequences on their fitness and behavior. Both T. canis and T. cati show similar migration patterns toward the central nervous system [143, 144], which may cause disorientation of paratenic hosts, ultimately favoring contact with the definitive hosts. Indeed, T. canis cause behavioral alterations and central nervous symptoms (e.g. dullness, somnolence, kyphosis, paresis, incoordination and tremor) in the infected mice, probably because of immune reactions rather than mechanical alterations [141, 145, 146 ]. Overall, these behavioral changes translate into a greater susceptibility to potential predators in the environment. In addition, the infection of the definitive hosts through predation of paratenic hosts has consequences on the time of larval development in adults, which is reduced (about 21 days) since larvae develop directly in the intestine without the liver-trachea-intestine migration route [147]. Also, invertebrates may carry Toxocara spp. larvae, including those of T. cati, though it is not clear whether these animals act as paratenic hosts or just carriers of hatched larvae in their gut (transport hosts), as already demonstrated for many taeniid eggs [148]. Finally, T. cati larvae have been shown to be released from the tissue of Rumina decollata snails [149], suggesting a role these mollusks may exert in the transmission of this ascarid through predation. This has been already demonstrated for metastrongylids A. abstrusus and T. brevior (feline lugworms) with snails, lizards and mice [119], also supported by the coinfections of these two groups of parasites in 18.6% cats from a multicenter European study [150]. In addiotn, Strongylida nematodes (Ancylostoma and Uncinaria), known as hookworms, cause cutaneous larva migrans in humans, dogs and cats, being more prevalent in tropical and subtropical regions [151]. Moreover, Ancylostoma caninum (Rhabditida: Ancylostomatidae) can also be associated with eosinophilic enteritis transmitted through the fecal-oral route [152]. Both A. caninum and Uncinaria stenocephala (Rhabditida: Ancylostomatidae) are usually transmitted orally through the ingestion of third-stage (L3) larvae in the environment or through the skin (percutaneous route) [153] and occasionally through the predation of paratenic hosts represented by rodents [154]. Indeed, it was demonstrated that L3s remain hypobiotic in rodents or other paratenic hosts such as monkeys [151].
Conclusions
The question of whether cats and dogs should be allowed to wander and have an outdoor lifestyle is an ongoing debate. However, the impact these animals have on the decline and extinction of wildlife populations of small animals (i.e. rodents, birds, reptiles and amphibians) is evident, as is the important role predation has on the transmission of zoonotic parasitic diseases. Three categories of dogs and cats are recognized depending on their contact with humans and healthcare (companion, stray and feral) and, consequently, the risk of preying on potential intermediate hosts of parasites. Although companion animals are more in contact with humans, and less with intermediate hosts, this category represents the major source of zoonotic transmission of parasites by means of fecal-oral infection, environmental contamination and owners’ contact with hunted prey. The main zoonotic parasitic diseases associated with predation are represented by protozoa (toxoplasmosis, acute muscular sarcocystosis, cryptosporidiosis), cestodes (mesocestoidiosis, alveolar echinococcosis, coenusiosis, sparganosis) and nematodes (visceral and cutaneous larva migrans). To date, control strategies for dog and cat populations are based on mass sterilization and sheltering of stray animals given that euthanasia and elimination are considered unethical. Thus, there is high permissiveness, mainly in western cultures, toward outdoor lifestyle of dogs and cats, which perpetuates the trophic transmission of zoonotic parasites. Predation, therefore, represents a potential risk for human health that should be addressed by stakeholders and public health officials on different levels (i.e. municipalities, regions, countries). Moreover, conscious and responsible ownership is pivotal for control programs to succeed. This includes education of owners and the community on proper deworming protocols, zoonotic parasites, diminishing outdoor access by offering enriched indoor environments, and collection and hygienic disposal of feces. Thus, it is important that veterinarians advocate for a regular and periodic deworming of all categories of dogs and cats to reduce or clear parasitic burden, eventually reducing environmental contamination. It is important to raise awareness about the zoonotic potential of parasites of dogs and cats associated with predation, not only of owners and veterinarians but also of medical practitioners. As discussed in this review, the trophic transmission of zoonotic parasites has been scarcely studied, given the difficulties in assessing the role of intermediate hosts as well as running field studies to evaluate the risk of transmission. However, future efforts should be performed to address the emergence or re-emergence of cats’ and dogs’ zoonotic parasites that depend on predation to update and improve control strategies. Creating awareness of pet owners, policy makers and scientists regarding the urgent need to reduce predation of intermediate or paratenic hosts by cats and dogs and the risk of zoonotic infection of parasites is ultimately the first step in creating a more conscious society.
Availability of data and materials
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References
Cecchetti M, Crowley SL, Goodwin CED, McDonald RA. Provision of high meat content food and object play reduce predation of wild animals by domestic cats Felis catus. Curr Biol. 2021;31:1107–11.
Cecchetti M, Crowley SL, McDonald J, McDonald RA. Owner-ascribed personality profiles distinguish domestic cats that capture and bring home wild animal prey. Appl Anim Behav Sci. 2022;256:105774.
Chevalier V, Davun H, Sorn S, Ly P, Pov V, Ly S. Large scale dog population demography, dog management and bite risk factors analysis: a crucial step towards rabies control in Cambodia. PLoS ONE. 2021;16:e0254192.
Fancourt BA, Augusteyn J, Cremasco P, Nolan B, Richards S, Speed J, et al. Measuring, evaluating and improving the effectiveness of invasive predator control programs: feral cat baiting as a case study. J Environ Manage. 2021;280:111691.
Wayne RK, Ostrander EA. Origin, genetic diversity, and genome structure of the domestic dog. BioEssays. 1999;21:247–57.
Frantz LA, Mullin VE, Pionnier-Capitan M, Lebrasseur O, Ollivier M, Perri A, et al. Genomic and archaeological evidence suggest a dual origin of domestic dogs. Science. 2016;352:1228–31.
Hu Y, Hu S, Wang W, Wu X, Marshall FB, Chen X, et al. Earliest evidence for commensal processes of cat domestication. Proc Natl Acad Sci USA. 2014;111:116–20.
Deak BP, Ostendorf B, Taggart DA, Peacock DE, Bardsley DK. The significance of social perceptions in implementing successful feral cat management strategies: a global review. Animals (Basel). 2019;9:617.
Ellingsen K, Zanella AJ, Bjerkås E, Indrebø A. The relationship between empathy, perception of pain and attitudes toward pets among Norwegian dog owners. Anthrozoös. 2010;23:231–43.
Wald DM, Jacobson SK, Levy JK. Outdoor cats: identifying differences between stakeholder beliefs, perceived impacts, risk and management. Biol Cons. 2013;167:414–24.
Chalkowski K, Wilson AE, Lepczyk CA, Zohdy S. Who let the cats out? A global meta-analysis on risk of parasitic infection in indoor versus outdoor domestic cats (Felis catus). Biol Lett. 2019;15:20180840.
Stella JL, Croney CC. Environmental aspects of domestic cat care and management: implications for cat welfare. Sci World J. 2016. https://doi.org/10.1155/2016/6296315.
Yeates J, Yates D. Staying in or going out? The dilemma for cat welfare. Vet Rec. 2017;180:193–4.
Loss SR, Boughton B, Cady SM, Londe DW, McKinney C, O’Connell TJ, et al. Review and synthesis of the global literature on domestic cat impacts on wildlife. J Anim Ecol. 2022;91:1361–72.
Hughes J, Macdonald DW. A review of the interactions between free-roaming domestic dogs and wildlife. Biol Conserv. 2020;157:341–51.
Loss SR, Will T, Marra PP. The impact of free-ranging domestic cats on wildlife of the United States. Nat Commun 2013; 4: 1396
Baker PJ, Bentley AJ, Ansell RJ, Harris S. Impact of predation by domestic cats Felis catus in an urban area. Mammal Rev. 2005;35:302–12.
Beckerman AP, Boots M, Gaston KJ. Urban bird declines and the fear of cats. Anim Conserv. 2007;10:320–5.
Levy JK, Crawford PC. Humane strategies for controlling feral cat populations. J A Vet Med Ass. 2004;225:1354–60.
Levy JK. Feral cat management. Shelter medicine for veterinarians and staff. Ames, IA: Blackwell Publishing; 2004. p. 377–88.
Young JK, Olson KA, Reading RP, Amgalanbaatar S, Berger J. Is wildlife going to the dogs? Impacts of feral and free-roaming dogs on wildlife populations. Bioscience. 2011;61:125–32.
Liccioli S, Giraudoux P, Deplazes P, Massolo A. Wilderness in the “city” revisited: different urbes shape transmission of Echinococcus multilocularis by altering predator and prey communities. Trends Parasitol. 2015;31:297–305.
Johnson PT, Dobson A, Lafferty KD, Marcogliese DJ, Memmott J, Orlofske SA, et al. When parasites become prey: ecological and epidemiological significance of eating parasites. Trends Ecol Evol. 2010;25:362–71.
Médoc V, Beisel JN. When trophically-transmitted parasites combine predation enhancement with predation suppression to optimize their transmission. Oikos. 2011;120:1452–8.
Seppälä O, Valtonen ET, Benesh DP. Host manipulation by parasites in the world of dead-end predators: adaptation to enhance transmission? Proc Royal Soc B. 2008;275:1611–5.
Vyas A, Kim SK, Giacomini N, Boothroyd JC, Sapolsky RM. Behavioral changes induced by Toxoplasma infection of rodents are highly specific to aversion of cat odors. Proc Natl Acad Sci USA. 2007;104:6442–7.
Dubey JP, Murata FHA, Cerqueira-Cézar CK, Kwok OCH, Su C. Epidemiological significance of Toxoplasma gondii infections in wild rodents: 2009–2020. J Parasitol. 2021;107:182–204.
Smith NC, Goulart C, Hayward JA, Kupz A, Miller CM, van Dooren GG. Control of human toxoplasmosis. Int J Parasitol. 2021;51:95–121.
Uttah E, Ogban E, Okonofua C. Toxoplasmosis: a global infection, so widespread, so neglected. Int J Sci Res. 2013;3:1–6.
Hansen-Wheat C, Fitzpatrick JL, Rogell B, Temrin H. Behavioural correlations of the domestication syndrome are decoupled in modern dog breeds. Nat Commun. 2019;10:2422.
Smith TD, Van Valkenburgh B. The dog-human connection. Anat Rec (Hoboken). 2021;304:10–8.
Driscoll CA, Macdonald DW, O’Brien SJ. From wild animals to domestic pets, an evolutionary view of domestication. Proc Natl Acad Sci USA. 2009;106:9971–8.
Montague MJ, Li G, Gandolfi B, Khan R, Aken BL, Searle SMJ, et al. Comparative analysis of the domestic cat genome reveals genetic signatures underlying feline biology and domestication. Proc Natl Acad Sci USA. 2014;111:17230–5.
Galibert F, Quignon P, Hitte C, André C. Toward understanding dog evolutionary and domestication history. C R Biol. 2011;334:190–6.
Bergström A, Stanton DWG, Taron UH, Frantz L, Sinding MS, Ersmark E, et al. Grey wolf genomic history reveals a dual ancestry of dogs. Nature. 2022;607:313–20.
Driscoll CA, Clutton-Brock J, Kitchener AC, O’Brien SJ. The Taming of the cat. Genetic and archaeological findings hint that wildcats became housecats earlier—and in a different place—than previously thought. Sci Am. 2009;300:68–75.
Kurushima JD, Ikram S, Knudsen J, Bleiberg E, Grahn RA, Lyons LA. Cats of the pharaohs: genetic comparison of egyptian cat mummies to their feline contemporaries. J Archaeol Sci. 2012;39:3217–23.
Lipinski MJ, Froenicke L, Baysac KC, Billings NC, Leutenegger CM, Levy AM, et al. The ascent of cat breeds: genetic evaluations of breeds and worldwide random-bred populations. Genomics. 2008;91:12–21.
Blaisdell JD. The rise of man’s best friend: the popularity of dogs as companion animals in late eighteenth-century London as reflected by the dog tax of 1796. Anthrozoös. 1999;12:76–87.
Pereira A, Martins Â, Brancal H, Vilhena H, Silva P, Pimenta P, et al. Parasitic zoonoses associated with dogs and cats: a survey of Portuguese pet owners’ awareness and deworming practices. Parasit Vectors. 2016;9:245.
Downes M, Canty MJ, More SJ. Demography of the pet dog and cat population on the island of Ireland and human factors influencing pet ownership. Prev Vet Med. 2009;92:140–9.
Jalongo MR. Pet keeping in the time of COVID-19: the canine and feline companions of young children. Early Child Educ J. 2021. https://doi.org/10.1007/s10643-021-01251-9.
Kretzler B, König HH, Hajek A. Pet ownership, loneliness, and social isolation: a systematic review. Soc Psychiatry Psychiatr Epidemiol. 2022;57:1935–57.
Contreras-Abarca R, Crespin SJ, Moreira-Arce D, Simonetti JA. Redefining feral dogs in biodiversity conservation. Biol Conserv. 2022;265:109434.
Baneth G, Thamsborg SM, Otranto D, Guillot J, Blaga R, Deplazes P, et al. Major parasitic zoonoses associated with dogs and cats in Europe. J Comp Pathol. 2016;155:S54-74.
Szwabe K, Błaszkowska J. Stray dogs and cats as potential sources of soil contamination with zoonotic parasites. Ann Agric Environ Med. 2017;24:39943.
Otranto D, Dantas-Torres F, Mihalca AD, Traub RJ, Lappin M, Baneth G. Zoonotic Parasites of sheltered and stray dogs in the era of the global economic and political crisis. Trends Parasitol. 2017;33:813–25.
Fang F, Li J, Huang T, Guillot J, Huang W. Zoonotic helminths parasites in the digestive tract of feral dogs and cats in Guangxi, China. BMC Vet Res. 2015;11:211.
Fancourt BA, Harry G, Speed J, Gentle MN. Efficacy and safety of Eradicat® feral cat baits in eastern Australia: population impacts of baiting programmes on feral cats and non-target mammals and birds. J Pest Sci. 2022;95:505–22.
Crawford HM, Calver MC, Fleming PA. A Case of letting the cat out of the bag-why trap-neuter-return is not an ethical solution for stray cat (Felis catus) management. Animals (Basel). 2019;9:171.
Grigg EK, Kogan LR. Owners’ attitudes, knowledge, and care practices: exploring the implications for domestic cat behavior and welfare in the home. Animals (Basel). 2019;9:978.
Ortega-Pacheco A, Jiménez-Coello M. Debate for and against euthanasia in the control of dog populations. Euthanasia—The “Good Death” controversy in humans and animals; Kure, J., Ed. 2011. p. 233–246.
Voslářvá E, Passantino A. Stray dog and cat laws and enforcement in Czech Republic and in Italy. Ann Ist Super Sanità. 2012;48:97–104.
Soldanescu TL. Illusory or effective? The protection provided by the Romanian authorities to stray dogs. AUBD. 2021;2021:23.
Debrot AO, Ruijter MN, Endarwin W, van Hooft P, Wulf K, Delnevo AJ. A renewed call for conservation leadership 10 years further in the feral cat Trap-Neuter-Return debate and new opportunities for constructive dialogue. Conserv Sci Pract. 2022;4:e12641.
Abdulkarim A, Khan M, Aklilu E. Stray animal population control: methods, public health concern, ethics, and animal welfare issues. World. 2021;11:319–26.
Barnett BD. Eradication and control of feral and free-ranging dogs in the Galapagos Islands. Proceedings of the vertebrate pest conference, vol 12(12). 1986.
Nogales M, Martín A, Tershy BR, Donlan CJ, Veitch D, Puerta N, et al. A review of feral cat eradication on islands. Conserv Biol. 2004;18:310–9.
Merz L, Kshirsagar AR, Rafaliarison RR, Rajaonarivelo T, Farris ZJ, Randriana Z, et al. Wildlife predation by dogs in Madagascar. Biotropica. 2022;54:181–90.
Dickman CR. House cats as predators in the Australian environment: impacts and management. Hum-wildl interact. 2009;3:41–8.
Sarvi S, Daryani A, Sharif M, Rahimi MT, Kohansal MH, Mirshafiee S, et al. Zoonotic intestinal parasites of carnivores: a systematic review in Iran. Vet World. 2018;11:58.
Deplazes P, van Knapen F, Schweiger A, Overgaauw PA. Role of pet dogs and cats in the transmission of helminthic zoonoses in Europe, with a focus on echinococcosis and toxocarosis. Vet Parasitol. 2011;182:41–53.
Bonnaud E, Bourgeois K, Vidal E, Kayser Y, Tranchant Y, Legrand J. Feeding ecology of a feral cat population on a small Mediterranean island. J Mammal. 2007;88:1074–81.
Loss SR, Marra PP. Population impacts of free‐ranging domestic cats on mainland vertebrates. Front Ecol Environ. 2017; 15:502–509.
Doherty TS, Dickman CR, Glen AS, Newsome TM, Nimmo DG, Ritchie EG, et al. The global impacts of domestic dogs on threatened vertebrates. Biol Conserv. 2017;210:56–9.
Henderson RW. Consequences of predator introductions and habitat destruction on amphibians and reptiles in the post-Columbus West Indies. Caribb J Sci. 1992;28:1–10.
Galbreath R, Brown D. The tale of the lighthouse-keeper’s cat: discovery and extinction of the Stephens Island wren (Traversia lyalli). Notornis. 2004;51:193–200.
Bonnaud E, Medina FM, Vidal E, Nogales M, Tershy B, Zavaleta E, et al. The diet of feral cats on islands: a review and a call for more studies. Biol Invasions. 2011;13:581–603.
Medina FM, Bonnaud E, Vidal E, Nogales M. Underlying impacts of invasive cats on islands: not only a question of predation. Biodivers Conserv. 2014;23:327–42.
Loss SR, Boughton B, Cady SM, Londe DW, McKinney C, O’Connell TJ, et al. Review and synthesis of the global literature on domestic cat impacts on wildlife. J Anim Ecol. 2022;91:1361–72.
Woinarski JC, South SL, Drummond P, Johnston GR, Nankivell A. The diet of the feral cat (Felis catus), red fox (Vulpes vulpes) and dog (Canis familiaris) over a three-year period at Witchelina Reserve, in arid South Australia. Aust Mammal. 2017;40:204–13.
Krauze-Gryz D, Gryz J, Goszczyński J. Predation by domestic cats in rural areas of central Poland: an assessment based on two methods. J Zool. 2012;288:260–6.
Tan SML, Stellato AC, Niel L. Uncontrolled outdoor access for cats: an assessment of risks and benefits. Animals (Basel). 2020;10:258.
Pirie TJ, Thomas RL, Fellowes MD. Pet cats (Felis catus) from urban boundaries use different habitats, have larger home ranges and kill more prey than cats from the suburbs. Landsc Urban Plan. 2022;220:104338.
Walker JK, Bruce SJ, Dale AR. A survey of public opinion on cat (Felis catus) predation and the future direction of cat management in New Zealand. Animals. 2017;7:49.
Stobo-Wilson AM, Murphy BP, Legge SM, Caceres-Escobar H, Chapple DG, Crawford HM, et al. Counting the bodies: estimating the numbers and spatial variation of Australian reptiles, birds and mammals killed by two invasive mesopredators. Divers Distrib. 2022;28:976–91.
Holderness-Roddam B, McQuillan PB. Domestic dogs (Canis familiaris) as a predator and disturbance agent of wildlife in Tasmania. Australas J Environ Manag. 2014;21:441–52.
Genovesi P. Impact of free ranging dogs on wildlife in Italy. Proc Vertebr Pest Conf. 2000;19:19.
Taborsky M. Kiwis and dog predation: observations in Waitangi State Forest. Notornis. 1988;35:197–202.
Doherty TS, Glen AS, Nimmo DG, Ritchie EG, Dickman CR. Invasive predators and global biodiversity loss. Proc Natl Acad Sci USA. 2016;113:11261–5.
Kikillus KH, Chambers GK, Farnworth MJ, Hare KM. Research challenges and conservation implications for urban cat management in New Zealand. Pac Conserv Biol. 2016;23:15–24.
Otranto D, Cantacessi C, Pfeffer M, Dantas-Torres F, Brianti E, Deplazes P, et al. The role of wild canids and felids in spreading parasites to dogs and cats in Europe. Part I: protozoa and tick-borne agents. Vet Parasitol. 2015;213:12–23.
Otranto D, Cantacessi C, Dantas-Torres F, Brianti E, Pfeffer M, Genchi C, et al. The role of wild canids and felids in spreading parasites to dogs and cats in Europe. Part II: helminths and arthropods. Vet Parasitol. 2015;213:24–37.
Hutchings MR, Judge J, Gordon IJ, Athanasiadou S, Kyriazakis I. Use of trade-off theory to advance understanding of herbivore–parasite interactions. Mamm Rev. 2006;36:1–16.
Frainer A, McKie BG, Amundsen PA, Knudsen R, Lafferty KD. Parasitism and the biodiversity-functioning relationship. Trends Ecol Evol. 2018;33:260–8.
Robertson ID, Thompson RC. Enteric parasitic zoonoses of domesticated dogs and cats. Microbes Infect. 2002;4:867–73.
Tull A, Valdmann H, Tammeleht E, Kaasiku T, Rannap R, Saarma U. High overlap of zoonotic helminths between wild mammalian predators and rural dogs—an emerging One Health concern? Parasitology. 2022;149:1565–74.
Wells K, Gibson DI, Clark NJ, Ribas A, Morand S, McCallum HI. Global spread of helminth parasites at the human-domestic animal-wildlife interface. Glob Chang Biol. 2018;24:3254–65.
Han BA, Castellanos AA, Schmidt JP, Fischhoff IR, Drake JM. The ecology of zoonotic parasites in the Carnivora. Trends Parasitol. 2021;37:1096–110.
Palmer CS, Robertson ID, Traub RJ, Rees R, Thompson RC. Intestinal parasites of dogs and cats in Australia: the veterinarian’s perspective and pet owner awareness. Vet J. 2010;183:358–61.
Dickman CR. Impact of exotic generalist predators on the native fauna of Australia. Wildlife Biol. 1996;2:185–95.
Berger L, Skerratt LF, Zhu XQ, Young S, Speare R. Severe sparganosis in Australian tree frogs. J Wildl Dis. 2009;45:921–9.
Khademvatan S, Abdizadeh R, Rahim F, Hashemitabar M, Ghasemi M, Tavalla M. Stray cats gastrointestinal parasites and its association with public health in Ahvaz City, South Western of Iran. Jundishapur J Microbiol. 2014. https://doi.org/10.5812/jjm.11079.
Overgaauw PA, van Zutphen L, Hoek D, Yaya FO, Roelfsema J, Pinelli E, et al. Zoonotic parasites in fecal samples and fur from dogs and cats in The Netherlands. Vet Parasitol. 2009;163:115–22.
Tamponi C, Knoll S, Tosciri G, Salis F, Dessì G, Cappai MG, et al. Environmental contamination by dog feces in touristic areas of italy: parasitological aspects and zoonotic hazards. Am J Trop Med Hyg. 2020;103:1143–9.
Lourido S. Toxoplasma gondii. Trends Parasitol. 2019;35:944–5.
Sroka J, Karamon J, Dutkiewicz J, Wójcik Fatla A, Zając V, Cencek T. Prevalence of Toxoplasma gondii infection in cats in southwestern Poland. Ann Agric Environ Med. 2018;25:576–80.
Nayeri T, Sarvi S, Daryani A. Toxoplasma gondii in mollusks and cold-blooded animals: a systematic review. Parasitology. 2021;148:895–903.
Italiano CM, Wong KT, AbuBakar S, Lau YL, Ramli N, Syed SF, et al. Sarcocystis nesbitti causes acute, relapsing febrile myositis with a high attack rate: description of a large outbreak of muscular sarcocystosis in Pangkor Island, Malaysia, 2012. PLoS Negl Trop Dis. 2014;8:e2876.
Tappe D, Ernestus K, Rauthe S, Schoen C, Frosch M, Müller A, et al. Initial patient cluster and first positive biopsy findings in an outbreak of acute muscular Sarcocystis-like infection in travelers returning from Tioman island, Peninsular Malaysia, in 2011. J Clin Microbiol. 2013;51:725–6.
Lau YL, Chang PY, Tan CT, Fong MY, Mahmud R, Wong KT. Sarcocystis nesbitti infection in human skeletal muscle: possible transmission from snakes. Am J Trop Med Hyg. 2014;90:361–4.
Legge S, Taggart PL, Dickman CR, Read JL, Woinarski JC. Cat-dependent diseases cost Australia AU $6 billion per year through impacts on human health and livestock production. Wildl Res. 2020;47:731–46.
Guo Y, Ryan U, Feng Y, Xiao L. Emergence of zoonotic Cryptosporidium parvum in China. Trends Parasitol. 2022;38:335–43.
Taghipour A, Olfatifar M, Bahadory S, Godfrey SS, Abdoli A, Khatami A, et al. The global prevalence of Cryptosporidium infection in dogs: a systematic review and meta-analysis. Vet Parasitol. 2020;281:109093.
Giangaspero A, Iorio R, Paoletti B, Traversa D, Capelli G. Molecular evidence for Cryptosporidium infection in dogs in Central Italy. Parasitol Res. 2006;99:297–9.
Taghipour A, Khazaei S, Ghodsian S, Shajarizadeh M, Olfatifar M, Foroutan M, et al. Global prevalence of Cryptosporidium spp. in cats: a systematic review and meta-analysis. Res Vet Sci. 2021;137:77–85.
Ramirez NE, Ward LA, Sreevatsan S. A review of the biology and epidemiology of cryptosporidiosis in humans and animals. Microbes Infect. 2004;6:773–85.
Köseoğlu AE, Can H, Karakavuk M, Güvendi M, Değirmenci Döşkaya A, Manyatsi PB, et al. Molecular prevalence and subtyping of Cryptosporidium spp. in fecal samples collected from stray cats in İzmir, Turkey. BMC Vet Res. 2022;18:89.
Yang R, Ying JL, Monis P, Ryan U. Molecular characterisation of Cryptosporidium and Giardia in cats (Felis catus) in Western Australia. Exp Parasitol. 2015;155:13–8.
Sapp SGH, Bradbury RS. The forgotten exotic tapeworms: a review of uncommon zoonotic Cyclophyllidea. Parasitology. 2020;147:533–58.
Polley L. Navigating parasite webs and parasite flow: emerging and re-emerging parasitic zoonoses of wildlife origin. Int J Parasitol. 2005;35:1279–94.
Széll Z, Tolnai Z, Sréter T. Environmental determinants of the spatial distribution of Mesocestoides spp. and sensitivity of flotation method for the diagnosis of mesocestoidosis. Vet Parasitol. 2015;212:427–30.
McAllister CT, Tkach VV, Conn DB. Morphological and molecular characterization of post-larval pre-tetrathyridia of Mesocestoides sp. (Cestoda: Cyclophyllidea) from ground skink, Scincella lateralis (Sauria: Scincidae), from southeastern Oklahoma. J Parasitol. 2018;104:246–53.
Voge M. North American cestodes of the genus Mesocestoides. Univ Calif Publ Zool. 1955;59:125–56.
Fincham JE, Seier JV, Verster A, Rose AG, Taljaard JJF, Woodroof CW, et al. Pleural Mesocestoides and cardiac shock in an obese vervet monkey (Cercopithecus aethiops). Vet Path. 1995;32:330–3.
Tokiwa T, Taira K, Yamazaki M, Kashimura A, Une Y. The first report of peritoneal tetrathyridiosis in squirrel monkey (Saimiri sciureus). Parasitol Int. 2014;63:705–7.
Di Filippo MM, Meoli R, Cavallero S, Eleni C, De Liberato C, Berrilli F. Molecular identification of Mesocestoides sp metacestodes in a captive gold-handed tamarin (Saguinus midas). Infect Genet Evol. 2018;65:399–405.
Parker GA, Ball MA, Chubb JC. Evolution of complex life cycles in trophically transmitted helminths. II. How do life-history stages adapt to their hosts? J Evol Biol. 2015;28:292–304.
Deplazes P, Hegglin D, Gloor S, Romig T. Wilderness in the city: the urbanization of Echinococcus multilocularis. Trends Parasitol. 2004;20:77–84.
Torgerson PR, Keller K, Magnotta M, Ragland N. The global burden of alveolar echinococcosis. PLoS Negl Trop Dis. 2010;4:e722.
Baumann S, Shi R, Liu W, Bao H, Schmidberger J, Kratzer W, et al. Worldwide literature on epidemiology of human alveolar echinococcosis: a systematic review of research published in the twenty-first century. Infection. 2019;47:703–27.
Hofer S, Gloor S, Müller U, Mathis A, Hegglin D, Deplazes P. High prevalence of Echinococcus multilocularis in urban red foxes (Vulpes vulpes) and voles (Arvicola terrestris) in the city of Zürich, Switzerland. Parasitology. 2000;120:135–42.
Dyachenko V, Pantchev N, Gawlowska S, Vrhovec MG, Bauer C. Echinococcus multilocularis infections in domestic dogs and cats from Germany and other European countries. Vet Parasitol. 2008;157:244–53.
Kern P, Ammon A, Kron M, Sinn G, Sander S, Petersen LR, et al. Risk factors for alveolar echinococcosis in humans. Emerg Infect Dis. 2004;10:2088–93.
Zhang XY, Jian YN, Ma LQ, Li XP, Karanis P. A Case of Coenurosis in a wild rabbit (Lepus sinensis) caused by Taenia serialis metacestode in Qinghai Tibetan plateau Area, China. Korean J Parasitol. 2018;56:195–8.
Trasviña-Muñoz E, López-Valencia G, Monge-Navarro FJ, Herrera-Ramírez JC, Haro P, Gómez-Gómez SD, et al. Detection of intestinal parasites in stray dogs from a farming and cattle region of Northwestern Mexico. Pathogens. 2020;9:516.
Conboy G. Cestodes of dogs and cats in North America. Vet Clin North Am Small Anim Pract. 2009;39:1075–90.
Torgerson PR, Macpherson CN. The socioeconomic burden of parasitic zoonoses: global trends. Vet Parasitol. 2011;182:79–95.
Badri M, Olfatifar M, KarimiPourSaryazdi A, Zaki L, Madeira de Carvalho LM, Fasihi Harandi M, et al. The global prevalence of Spirometra parasites in snakes, frogs, dogs, and cats: a systematic review and meta-analysis. Vet Med Sci. 2022;8:2785–805.
Mendoza-Roldan JA, Modry D, Otranto D. Zoonotic parasites of reptiles: a crawling threat. Trends Parasitol. 2020;36:677–87.
Kuchta R, Kołodziej-Sobocińska M, Brabec J, Młocicki D, Sałamatin R, Scholz T. Sparganosis (Spirometra) in Europe in the Molecular Era. Clin Infect Dis. 2021;72:882–90.
Liu W, Gong T, Chen S, Liu Q, Zhou H, He J, et al. Epidemiology, diagnosis, and prevention of sparganosis in Asia. Animals (Basel). 2022;12:1578.
Bezerra-Santos MA, Mendoza-Roldan JA, Abramo F, Lia RP, Tarallo VD, Salant H, et al. Transmammary transmission of Troglostrongylus brevior feline lungworm: a lesson from our gardens. Vet Parasitol. 2020;285:109215.
Giannelli A, Colella V, Abramo F, do Nascimento Ramos RA, Falsone L, Brianti E, et al. Release of lungworm larvae from snails in the environment: potential for alternative transmission pathways. PLoS Negl Trop Dis. 2015;9:e0003722.
Morgan ER, Shaw SE, Brennan SF, De Waal TD, Jones BR, Mulcahy G. Angiostrongylus vasorum: a real heartbreaker. Trends Parasitol. 2005;21:49–51.
Riggio F, Mannella R, Ariti G, Perrucci S. Intestinal and lung parasites in owned dogs and cats from central Italy. Vet Parasitol. 2013;193:78–84.
Wu TK, Bowman DD. Toxocara canis. Trends Parasitol. 2022;38:709–10.
Hotez PJ, Wilkins PP. Toxocariasis: America’s most common neglected infection of poverty and a helminthiasis of global importance? PLoS Negl Trop Dis. 2009;3:e400.
Taira K, Saeed I, Permin A, Kapel CM. Zoonotic risk of Toxocara canis infection through consumption of pig or poultry viscera. Vet Parasitol. 2004;121:115–24.
Schnieder T, Laabs EM, Welz C. Larval development of Toxocara canis in dogs. Vet Parasitol. 2011;175:193–206.
Strube C, Heuer L, Janecek E. Toxocara spp. infections in paratenic hosts. Vet Parasitol. 2013;193:375–89.
Oryan A, Sadjjadi SM, Azizi S. Longevity of Toxocara cati larvae and pathology in tissues of experimentally infected chickens. Korean J Parasitol. 2010;48:79–80.
Burren CH. The distribution of Toxocara canis larvae in the central nervous system of rodents. Trans R Soc Trop Med Hyg. 1972;66:937–42.
Glickman LT, Schantz PM. Epidemiology and pathogenesis of zoonotic toxocariasis. Epidemiol Rev. 1981;3:230–50.
Alba-Hurtado F, Muñoz-Guzmán MA, Valdivia-Anda G, Tórtora JL, Ortega-Pierres MG. Toxocara canis: larval migration dynamics, detection of antibody reactivity to larval excretory-secretory antigens and clinical findings during experimental infection of gerbils (Meriones unguiculatus). Exp Parasitol. 2009;122:1–5.
Akao N, Tomoda M, Hayashi E, Suzuki R, Shimizu-Suganuma M, Shichinohe K, et al. Cerebellar ataxia due to Toxocara infection in Mongolian gerbils, Meriones unguiculatus. Vet Parasitol. 2003;1:229–37.
Overgaauw PAM, Nederland V. Aspects of Toxocara epidemiology: toxocarosis in dogs and cats. Crit Rev Microbiol. 1997;23:233–51.
Benelli G, Wassermann M, Brattig NW. Insects dispersing taeniid eggs: who and how? Vet Parasitol. 2021;295:109450.
Cardillo N, Prous CG, Krivokapich S, Pittaro M, Ercole M, Perez M, et al. First report of Toxocara cati in the domestic land snail Rumina decollata. Rev Argent Microbiol. 2016;48:206–9.
Giannelli A, Capelli G, Joachim A, Hinney B, Losson B, Kirkova Z, et al. Lungworms and gastrointestinal parasites of domestic cats: a European perspective. Int J Parasitol. 2017;47:517–28.
Bowman DD, Montgomery SP, Zajac AM, Eberhard ML, Kazacos KR. Hookworms of dogs and cats as agents of cutaneous larva migrans. Trends Parasitol. 2010;26:162–7.
Prociv P, Croese J. Human eosinophilic enteritis caused by dog hookworm Ancylostoma caninum. Lancet. 1990;335:1299–302.
Massetti L, Wiethoelter A, McDonagh P, Rae L, Marwedel L, Beugnet F, et al. Faecal prevalence, distribution and risk factors associated with canine soil-transmitted helminths contaminating urban parks across Australia. Int J Parasitol. 2022;52:637–46.
Otranto D, Deplazes P. Zoonotic nematodes of wild carnivores. Int J Parasitol Parasites Wildl. 2019;9:370–83.
Acknowledgements
The authors thank Riccardo Paolo Lia (Department of Veterinary Medicine, University of Bari, Italy) for optical microscopy images used in figures.
Funding
This review has been conducted under the frame of the NextGenerationEU-MUR PNRR Extended Partnership initiative on Emerging Infectious Diseases (project no. PE00000007, INF-ACT).
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Investigation: JAMR and DO. Writing—original draft preparation: JAMR and DO. Writing—review and editing: JAMR and DO. All authors have read and approved of the final manuscript.
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Mendoza Roldan, J., Otranto, D. Zoonotic parasites associated with predation by dogs and cats. Parasites Vectors 16, 55 (2023). https://doi.org/10.1186/s13071-023-05670-y
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DOI: https://doi.org/10.1186/s13071-023-05670-y