Factors impacting on progress towards elimination of transmission of schistosomiasis japonica in China.

Over the past decades China has made a great stride in controlling schistosomiasis, eliminating transmission of Schistosoma japonicum in 5 provinces and remarkably reducing transmission intensities in the rest of the seven endemic provinces. Recently, an integrated control strategy, which focuses on interventions on humans and bovines, has been implemented throughout endemic areas in China. This strategy assumes that a reduction in transmission of S. japonicum from humans and bovines to the intermediate Oncomelania snail host would eventually block the transmission of this parasite, and has yielded effective results in some endemic areas. Yet the transmission of S. japonicum is relatively complicated--in addition to humans and bovines, more than 40 species of mammalians can serve as potential zoonotic reservoirs. Here, we caution that some factors--potential roles of other mammalian reservoirs and human movement in sustaining the transmission, low sensitivity/specificity of current diagnostic tools for infections, praziquantel treatment failures, changes in environmental and socio-economic factors such as flooding in key endemic areas--may pose great obstacles towards transmission interruption of the parasite. Assessing potential roles of these factors in the transmission and implications for current control strategies aiming at transmission interruption is needed.

Review

Background

Worldwide, Schistosoma infections remain a serious public health problem, infecting more than 200 million people in approximately 76 countries with a loss of 1·53 million disability-adjusted life years (DALYs) [1,2]. Of the species of schistosomes infecting humans, Schistosoma japonicum, distributed in southern China, the Philippines, and parts of Indonesia, is the only schistosome species whose transmission is zoonotic [1]. China’s schistosomiasis control program was initiated in the mid-1950s, and has undergone three stages [3-8]. The first stage (from the mid-1950s to mid-1980s) focused on transmission control, and the control program included chemotherapy, snail control primarily by environmental management or the use of molluscicide, improving access to clean water and sanitary facilities [3,5]. By the end of the 1980s, schistosomiasis transmission was eliminated in four endemic provinces but the prevalence of disease remained high in the rest of eight endemic provinces [3,5]. The second stage (from the mid-1980s to the early 2000s) focused on morbidity control, and large-scale chemotherapy (due to the introduction of praziquantel) served as the backbone of The National Schistosomiasis Control Program, which was complemented with health education and continued snail control [3-8]. In the mid-1990s, schistosomiasis transmission was eliminated in one of the remaining eight endemic provinces [3]. Despite continued and intensified control efforts, controlling transmission of the disease in the remaining seven endemic provinces (Hubei, Hunan, Anhui, Jiangxi, Jiangsu Sichuan and Yunnan provinces) has been challenging, and, eliminating the transmission in these regions seems a daunting task [3]. A number of studies reported that bovines are the primary infection source of S. japonicum transmission in China [3,9-12]. Based on this, the third stage of control, also called integrated control, aiming at reducing the roles of bovines and humans as infection sources, has been implemented in China since 2005. With renewed emphasis on transmission control and ultimately transmission interruption, control programs at this stage consist of agricultural mechanization, fencing bovines (particularly water buffalos), chemotherapy on both humans and bovines, health education, provision of clean water and improved sanitation [3]. This national strategy has so far achieved promising results and two notable patterns have been observed - in some endemic areas the prevalence of S. japonicum infection in humans was brought below 1% [3,13], whereas in other endemic regions with implementation of the same strategy, human infections were sustained at around 3% [3,14]. More recently, there was a discussion on the generalizability of this national integrated strategy to control and eventually interrupt the transmission of S. japonicum, which was based on the studies in lake regions of China, and in hilly and mountainous regions of Sichuan and Yunnan the transmission ecology is quite different [15]. Concern has been raised that, in addition to humans and bovines, there might be other factors that implicate the transmission but are neglected [14,16,17]. Here we summarize these factors based on a systematic review of published literature and focus on non-bovine animal hosts, human movements, low sensitivity/specificity of current diagnostic tools for schistosome infection, and praziquantel treatment failure and their implications for the current schistosomiasis control strategy in China. The following databases were used for identifying relevant articles: PubMed, Cochrane Library, Science Citation Index Expanded, China National Knowledge Infrastructure, Wanfang Database, VIP Database, and ProQuest. No restriction was applied to year of publication. All titles and abstracts were independently examined and screened by two reviewers to check their eligibility for inclusion in the review. An article was included in the tables of this paper if it met one of the following criteria included: (1) report on prevalence of infection of S. japonicum in non-bovine animal hosts in China; (2) report on prevalence of infection of S. japonicum in migrant populations in China. Upon inclusion, full papers were retrieved and reviewed by the same two reviewers.

Non-bovine animal hosts

S. japonicum, unlike S. mansoni and S. haematobium, is widely recognized as a zoonotic parasite. Over 40 species of wild and domesticated animals can serve as reservoir hosts for this parasite [9]. The zoonotic nature of S. japonicum complicates control efforts for the parasite. In China a number of non-human mammalian hosts, such as bovines, pigs, dogs, cats, goats/sheep, and rats, can serve as reservoir hosts and are of potential public health importance (Table 1) [10,11,16,18-26]. In addition to bovines, relatively high infection levels were also found in other mammalian hosts in some endemic areas (Table 1) [10,11,16,18-26]. High prevalences of S. japonicum infections in rats (59.8%) and in Oncomelania snails (0.4-3.1%) were reported in two islands located in the Yangtze River [19]. The two islands have only emerged in the last 40 years, humans do not inhabit these islands. High infections together with estimates of high transmission index (measured by excreted eggs per day) were also reported in dogs, cats, and rats in a hilly area of China where no infected bovines were found [16]. A similar pattern was also reported in Samar Province, the Philippines, where high prevalences and intensities of S. japonicum infection were also observed in dogs (14.9% prevalence) and rats (29.5% prevalence), suggesting that dogs could potentially be a very important reservoir host of S. japonicum in that region [27,28]. A modeling study indicated that rats may also play a role in human infections in Samar [27]. These findings suggested that the transmission of S. japonicum might occur in the absence of bovines. In addition, high genetic variation in S. japonicum was found in the marshland and lake endemic regions of China (where bovines are considered as an important source of infection) and two main genetic clusters were discovered, separating the strain in bovines and humans from that in goats, dogs, pigs and cats [18]. The result indicated that S. japonicum from bovines and humans might be different from that from other mammalian animals in lake and marshland areas of southern China. Also notable was that the prevalence of S. japonicum infection in pigs, dogs and cats increased when the bovines with high prevalence of infection were removed from the endemic area [16]. The strain from bovines and humans may be more prevalent than those from other mammalian animals in lake and marshland areas of southern China. When the predominant strain is completely or partly removed from endemic areas, the other strain may become predominant. Further studies are needed to address this question, for example, molecular epidemiological research should be performed to address whether the strains cross-infect humans and evaluate relative contribution of different animal reservoirs to sustain the transmission. Without improved knowledge on these issues, the reliance of human- and bovine-oriented control to achieve full control of infection sources might miss some other important sources of infection.

Table 1

Reported prevalence of infection of among different non-human hosts in China

Author and date of publication	Environmental type	Definitive hosts
		Bovine	Pig	Dog	Goat/sheep	Cat	Donkey	Horse	Mule	Rodent	Rabbit
Lu DB et al. (2010) [16]	Marshland*	35·5	0·0	4·8	55·0	0·0	-	-	-	0·0	-
	Marshland†	-	3·9	8·4	-	37·5	-	-	-	-	-
	Hill*	0·0	0·0	18·9	-	2·6	-	-	-	26·5	-
	Hill†	-	0·0	21·1	-	5·3	-	-	-	17·7	-
Wang TP et al. (2006) [18]	Marshland‡	26·9	7·4	2·7	33·3	0·0	-	-	-	-	-
	Marshland§	15·4	0·0	4·1	0·0	1·5	-	-	-	-	-
Xu GY et al. (1999) [19]	Marshland	-	-	-	-	-	-	-		59·8	-
Wang TP et al. (1997) [20]	Marshland	48·7	21·3	0·7	13·0	0·0	-	-	-	8·3	18·2
Sun LP et al. (1997) [21]	Marshland	22·1	26·7	-	-	-	-	-	-	-	-
Xu FS et al. (1995) [22]	Mountain	36·9	-	3·0	-	-	-			-	-
Su ZW et al. (1994) [23]	Lake	35·7	60·0	75·0	-	-	-	-	-	-	-
Gu XG et al. (1993) [24]	Mountain	36·9	-	3·0	-	-	-	-	-	0·9	-
Dai ZJ et al. (1991) [10]	Mountain	42·3	6·7	7·5	8·5	-	-	13·5	-	-	-
Zheng J et al. (1990) [11]	Mountain	17·3	13·2	8·2	4·2	0·0	4·3	3·4	3·2	1·4	-
Chen DJ et al. (1989) [25]	Mountain	15·2	17·1	75·0	10·8	-	-	4·7	-	57·1	-
Yao BY et al. (1989) [26]	Mountain	16·5	9·3	9·6	0·0	0·0	1·8	1·4	3·5	1·7	-

Note: * = 2006; †=2007; ‡= Chenqiao village; § = Guanghui village.

Human movement

The second potential obstacle in moving towards the elimination of schistosomiasis transmission relates to human movement. Along with China’s rapid economic development and urbanization over the past decades, the country has witnessed the largest human movement, in particular rural–urban migration in the human history (Table 2) [29-37]. For example, the movement population of rural migrants moving to coastal cities is approximately 120 million [38]. Meanwhile, large population movements are also occurring between cities, in particular from small cities to big cities [38]. It has long been recognized that human movement plays an important role in the epidemiology of many infectious diseases [38-40]. For example, some infectious diseases (e.g. leishmaniasis, Chagas disease, lymphatic filariasis, and schistosomiasis) have emerged or re-emerged in urban areas or previously controlled regions, which have been linked to human movements [38,41].

Table 2

Prevalence of infection of in different migrant populations

Author and date of publication	Movement type	Proportion of migration (%)	Prevalence (%)
Chen GX et al. (2011) [29]	Migration from endemic areas to other areas	22·4-38·5	2·6-5·3
Wang ZC et al. (2008) [30]	Migration from non-endemic areas to endemic areas	>5·3	12·5
He JC et al. (2008) [31]	Migration from endemic areas to other areas	-	3·2
	Migration from non-endemic areas to endemic areas	-	3·0
Zhang YQ et al. (2003) [32]	Migration from endemic areas to other areas	29·9	26·0
Li YS et al. (2003) [33]	Fishing population	-	68·9
Chen GX et al. (2001) [34]	Migration from endemic areas to other areas	19·7	15·6
Zhang SQ et al. (1998) [35]	Migration from endemic areas to other areas	19·8-32·4	2·1-13·9
Zheng J et al. (1999) [36]	Fishing population	-	18·2-84·2
	Boatman	-	54·2-69·4
	Herdsman	-	41·2
Ross AG et al. (1997) [37]	Fishing population	-	22·4

The occurrence of schistosome transmission in urban areas or re-emergence of the transmission in previously controlled areas were most probably through infected migrants and endemic foci was present in large cities such as in Bamako, Kampala, Changsha and Dar el Salam [38,41]. The impact of human migration on the transmission of schistosomiasis has been reported. For example, a report in Brazil indicated that migrants play an important role in the transmission of schistosomiasis, and the presence of mobile populations (e.g. migrants, returnees and tourists) in endemic regions can also impact significantly on the control effectiveness of schistosomiasis due to insufficient health services [42]. Yet, this potential remains largely unknown in China. In addition to lack of information on the spatial and temporal patterns of population movements, little is available on the epidemiological impact of the movement patterns on transmission and maintenance of schistosomiasis in China. Hence, studies to understand how human movements (e.g. between endemic and endemic areas, endemic and non-endemic areas) impact the transmission and control are needed. In addition to human movement, livestock movement (e.g. through livestock trade or movement to new grazing fields) also occurs frequently in endemic regions in China [42], and this raises another concern for the current national control strategy.

Diagnostic tests

While extensive control efforts in endemic areas have greatly suppressed the transmission levels, selective chemotherapy with praziquantel focusing on infected individuals becomes an important component of the national control program, and thus diagnosis of infection is a key step for determination of target populations for treatment, evaluation of morbidity, and assessment of control measures [43]. With decreasing infection intensities due to extensive control efforts, widely used direct parasitological techniques (e.g. miracidium hatch test (MHT) and Kato-Katz thick smear (KK)) have become increasingly insensitive [43]. KK and MHT are the two widely field-applied direct parasitological methods in China. The sensitivity of KK method ranges generally from 40% to 70%, while for MHT it varies from 24% to 95%, depending primarily on the levels of infection intensities [43]. The sensitivities of these direct parasitological techniques decrease generally with decrease in infection levels of humans. The insensitivities of KK and MHT methods lead to missing diagnosis of infected cases in areas of low endemicity, and in post-treatment situations. Other widely field-applied diagnostic alternatives are indirect immunodiagnostic assays (i.e. detecting schistosome-specific antibodies), e.g. Circumoval precipitin test (COPT), Indirect hemagglutination assay (IHA), Enzyme-linked immunosorbent assay (ELISA) and Dipstick dye immunoassay (DDIA). These antibody detection assays have relatively high sensitivities, but generally low specificities. The specificity varies widely for each test - 55% to 96% for COPT method, 35% to 94% for IHA method, 20% to 93% for ELISA method, and 33% to 97% for DDIA [43]. These antibody detection techniques cannot differentiate between current and past infections. Thus, the insensitivity or non-specificity of the currently field-applied diagnostic methods may result in difficulties in identifying true infected individuals for selective chemotherapy and assessing the effectiveness of interventions, collectively posing a significant obstacle in moving towards complete control of schistosomiasis. There are many other diagnostic methods such as clinical or ultrasonographic methods measuring the morbidity associated Schistosomiasis japonica, questionnaires, direct immunological tests detecting the schistosome-derived antigens, and the histological methods detecting schistosome eggs in tissue biopsies, but clinical or ultrasonographic methods, and questionnaires lack specificity in some areas such as China [43]. Although the circulating antigen detection assays have a relatively high specificity, they are not any better than the egg detection assays in terms of sensitivity in areas of low endemicity [44-47]. The histological diagnostic method with both high sensitivity and high specificity is neither simple nor convenient for population-based investigations. Recently, polymerase chain reaction (PCR) based techniques for detection of schistosome DNA in stool or sera and plasma have been developed, showing promise as a highly sensitive and specific assay for diagnosis of schistosome infection [48-55].

Other neglected factors

Other neglected factors (e.g. praziquantel treatment failures, frequent flooding, and environmental and socio-economic changes) may also pose challenges to the current control program. The praziquantel treatment failures include treatment non-compliance and drug resistance. The chemotherapy with praziquantel has been implemented widely in endemic regions in China since the 1990s, especially during the 10-year World Bank Loan Project (WBLP) [56]. The compliance rates of chemotherapy drop in many communities after repeated rounds of mass or selective treatment [57]. Although currently there is no evidence of praziquantel resistance for S. japonicum, the resistance is found in other schistosoma species (e.g. S. mansoni) [56]. Frequent flooding along the Yangtze River and in the lake regions (e.g. Dongting Lake and Poyang Lake regions) have contributed to the spread of the intermediate host Oncomelania hupensis, and might counteract control efforts [4]. Environmental changes, caused by returning reclaimed land to the lake, construction and operation of Three Gorges dam, and the South-to-North water transfer project, might create new habitats for O. hupensis[4,58].

Discussion

Although bovines are largely responsible for transmission of S. japonicum in the lake and marshland regions of China, they are a major source of incomes for local farmers. The large marshland areas of Dongting Lake and Poyang Lake are a natural and ideal pasture for bovines and goats, and provide natural habitats for the intermediate snail host. It is difficult to remove all bovines from or completely fence pastures on the large marshland areas, since the farmers have herded bovines, especially water buffaloes, in the marshland areas for generations [17]. Even if all bovines were removed from or well fenced from the large marshland areas some time, it is also challenging to maintain the state of “without bovines” on the marshland areas for a long period of time because bovine movement also occurs frequently in the lakes and marshland regions due to livestock trade or new grazing fields [59]. So, fencing pastures or removing bovines often conflicts with the traditional way of raising livestock (especially water buffalo) and farmers’ incomes, and this considerable conflict might reduce the control efforts of the ongoing integrated control strategy, as fencing pastures is one of the key technical measures of the control strategy [3]. Hence, this integrated control strategy should be implemented in the light of local conditions of endemic areas for mutual benefit and development. For example, the environmental management should be encouraged to be implemented in some snail-inhabited marshland areas suitable for agricultural or forestry practices (e.g., Cropping cole or wheat, planting trees for controlling snails), thus, the farmers not only might increase their incomes, but also bovines could be well fenced by these modified snail-inhabited marshland areas, and snails could be controlled by the environmental management.

Although much is known about migration in China, the typology of population movement is complex and remains less well characterized [40]. There are at least two types of population movements related to schistosomiasis transmission in China (Table 2) [29-37]: a) fishermen, boatmen and herders who move around in rivers or lakes; b) People moving seasonally for paid work (e.g. 1) people from endemic areas moving into other endemic regions; 2) people from non-endemic areas moving to endemic areas; 3) from endemic areas to controlled areas; 4) from endemic areas to non-endemic areas but back to endemic areas). Tens of thousands of fishermen, boatmen and herders, with a high prevalence and intensity of S. japonicum infection, move around in Dongting Lake and Poyang Lake which are strongholds of schistosomiasis endemic areas in China (Table 2) [33,36,37]. These people frequently contact infected water, and their stools generally go into the water or snail habitats directly. It has been well-known that these migrant fishermen and bovines are responsible for a large proportion of the total contamination of the environment with Schistosoma eggs and are hence drivers in maintaining transmission of the disease in the lake and marshland areas of southern China [33]. The administration of chemotherapy or stool collection for these nomads is very difficult and little is known about the optimal treatment window for these nomads. Seasonal mobility for paid work has been very common in recent years in China, e.g. some rural young labourers from endemic areas leave their homes in the slack season (in farming), and return in the busy season (in farming), and other migrants only return to their home annually in the Chinese New Year. Some labourers from non-endemic regions enter endemic areas for agriculture in the busy season and leave in the slack season. In the current national control program of schistosomiasis, praziquantel-based chemotherapy is implemented generally only in endemic areas in autumn each year (i.e. slack season for farming), and the target population of chemotherapy is usually the local residents, not non-local people [3,14]. So, most of migrants infected with S. japonicum are missed for the treatment, and continue to be the infection sources. Hence, the target population and time of chemotherapy in the national control program of schistosomiasis should be adjusted in light of the patterns of population movement, for example, the target population of chemotherapy should include the non-local people infected with S. japonicum, and chemotherapy should also be implemented in the Chinese New Year when most of the infected migrants return to their home for the Spring Festival.

It is unclear whether schistosomiasis transmission could be maintained by these neglected factors in the absence of bovines. To address this question further study is needed, and the long-term effectiveness of the comprehensive national strategy should be also further evaluated [9]. For example, some longitudinal studies should be carried out to determine or evaluate whether these neglected factors are important for S. japonicum transmission.

Conclusion

The current integrated strategy in China assumed that blocking the transmission of S. japonicum from human and cattle to snails would stem the transmission of this parasite [13]. Yet, the process of S. japonicum transmission is, in fact, relatively complicated, and might be abetted by other domesticated (e.g. dogs, cats, and goats) and wild (e.g. rats, and rabbits) animals, by population movement, and by social and hydrologic (e.g. flooding) links among some focal ‘hot spots’ of transmission. While we are working towards the transmission elimination of S. japonicum, these factors, which are currently neglected in the integrated strategy, need to be paid some attention by public health authorities.

Competing interests

The authors declare that they have no competing interests.

Authors’ contributions

YBZ, SL and QWJ wrote the manuscript together, YBZ summarized the Tables and all authors have read and approved the final version of the manuscript.