Literature DB >> 34665821

Soil-transmitted helminthiasis in China: A national survey in 2014-2015.

Ying-Dan Chen1,2,3,4, Men-Bao Qian1,2,3,4,5, Hui-Hui Zhu1,2,3,4, Chang-Hai Zhou1,2,3,4, Ting-Jun Zhu1,2,3,4, Ji-Lei Huang1,2,3,4, Zhong-Jie Li6, Shi-Zhu Li1,2,3,4,5, Xiao-Nong Zhou1,2,3,4,5.   

Abstract

BACKGROUND: Based on two national surveys, the prevalence of soil-transmitted helminthiasis (STH) in China had decreased from 53.58% in 1988-1992 to 19.56% in 2001-2004. To update the epidemiology and characteristics of STH in China, a third national survey was implemented in 2014-2015. METHODOLOGY/PRINCIPAL
FINDINGS: This survey covered rural areas in 31 provinces in mainland of China. Multiple-stage stratified cluster sampling was employed, which included three levels (provinces, ecozones and economical levels). Stool samples were collected and the Kato-Katz method was applied for helminth eggs detection. Samples with hookworm eggs were selected and hatched to differentiate the species based on larval morphology. Between June 2014 and May 2015, a total of 484,210 participants from 604 counties were enrolled. The weighted prevalence of STH overall was 4.49% (95% confidential interval (CI): 2.45%-6.53%), including 2.62% (95% CI: 0.86%-4.38%) hookworm infections, 1.36% (95% CI: 0.49%-2.23%) ascariasis, and 1.02% (95% CI: 0.15%-1.89%) trichuriasis. The estimated population infected was 29.12 million (95% CI: 15.88 million-42.32 million) for all STH; 16.97 million (95% CI: 5.57 million-28.39 million) for hookworm infections; 8.83 million (95% CI: 3.18 million-14.45 million) for ascariasis; and 6.60 million (95% CI: 0.97 million-12.25 million) for trichuriasis. Overall, the prevalence of ascariasis and trichuriasis was relatively high in children, while hookworm infections were more common in the older population, especially those over 60. STH was highly prevalent in western China, and moderately in central areas, but low in eastern and northern regions. Out of 3,579 hookworm cases with species differentiation, 479 cases (13.38%) were infected with only Ancylostoma spp., 2,808 cases (78.46%) with only Necator americanus, and another 292 cases (8.16%) with both species.
CONCLUSIONS/SIGNIFICANCE: This survey demonstrated the continuous decrease of STH in rural China. However, endemicity still prevails in the western areas of the country. Hookworm, especially N. americanus, is becoming the predominant species. Older farmers in western China should be prioritized for control due to the high prevalence of hookworm.

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Year:  2021        PMID: 34665821      PMCID: PMC8555824          DOI: 10.1371/journal.pntd.0009710

Source DB:  PubMed          Journal:  PLoS Negl Trop Dis        ISSN: 1935-2727


Introduction

Soil-transmitted helminthiasis (STH) constitutes a group of helminth diseases caused by Ascaris lumbricoides, Trichuris trichiura and hookworm (Ancylostoma spp. and Necator americanus), which still imposes a significant health burden [1,2]. Of the neglected tropical diseases, STH are the most prevalent, producing a total of 3.38 million disability-adjusted life years in 2015, out of which ascariasis, trichuriasis and hookworm infections contributed 1.08 million, 0.54 million and 1.76 million, respectively [3]. Due to continuing transmission favoured by the predominant tropical environment and the still low social and economic development, their prevalence in Asia, Africa and Latin America remains high [4-6]. Related to the productive activities, adults are usually highly susceptible to hookworm infections, while A. lumbricoides and T. trichiura are more common in children [4-6]. STH used to be a widespread, serious threat to public health in China. Two national surveys of intestinal helminthiasis using the Kato-Katz method were carried out in mainland of China in 1988–1992 and 2001–2004 [7,8]. The results of the first survey, showed that altogether 646 million were infected with prevalence rates of all STH, ascariasis, trichuriasis and hookworm infections amounting to 53.58%, 47.00%, 18.80% and 17.17%, respectively [7]. At the time of the second survey, the corresponding prevalence rates had declined to 19.56%, 12.72%, 4.63%, and 6.12%, with the total cases estimated at about 129 million [8]. Due to the difference in natural environment as well as economic development, STH is more common in western and southern China [7,8]. Spot checks carried out between 2006 and 2013 have established a continued general decline of STH from 20.88% to 3.12% [9,10]. To capture the updated national epidemiology of these infections, a third national survey to guide the final strategy and steps of the national STH control programme was implemented in rural China in 2014–2015.

Material and methods

Ethics statement

The study was approved by the ethics committees in the National Institute of Parasitic Diseases at Chinese Center for Disease Control and Prevention. The objectives, procedures and potential risks of this study were orally explained and informed to all participants. A written consent form was also obtained with signature of the participant or his/her guardian for a child.

Study design

This was a national cross-sectional sampling survey, covering 31 provinces in mainland of China. In consideration of the extreme low prevalence of STH in urban areas owing to high coverage of clean water and sanitation, only rural areas were covered for STH in this survey. A multiple-stage stratified cluster sampling strategy was employed, involving with three levels (provinces, ecozones and economic levels).

Sampling

The province level was treated as the main stratum followed by all types of ecozones in each province as the 1st substratum. The ecozones were defined based on type and natural environment according to the Ecozone Classification in China [11]. An ecozone usually covers several neighboring provinces and a province usually contains several different types of ecozones. Nationally, 50 ecozones are classified, but we included only 46 of them while the other four with very limited population were combined into neighboring ones. The sampling size was calculated for each 1st substratum using binomial distribution as well as the expected prevalence data. The expected prevalence referred to the data from a post-survey spot checks (in 22 selected provinces carried out in 2012). An expected prevalence of 1% was set in the other nine provinces where the endemic level of infection was perceived as low although not backed by actual surveillance data. Additionally, the same expected prevalence was set for all of 1st substrata in the same province. An allowance error was set at 10%, 15% and 30% when the expected prevalence was > 20%, 5%-20% and < 5%, respectively. Finally, an increase of 50% was used for the sample size. Below the 1st substratum level, the counties made up the 2nd substratum. They were classified into three levels based on the economic level as expressed by the rural net income per capita, which was provided by the local economic departments. According to the share of total rural population in the 1st substratum, the sampling size was distributed proportionally with respect to the 2nd substratum. The sampling unit was set as the natural village, i.e. a rural collection of houses comprising about 250 villagers, and the number of sampling units in each of the 2nd substratum as calculated. Usually, 3 units were included in each selected county. If the number was not integral, 2 or 4 units were selected. Thus, the number of counties needed to be sampled was decided there and then. In each sampled county, all towns were classified into 2–4 groups based on economic and natural conditions, then one town was sampled from each group. As a rural town is usually made up by dozens of natural villages, one natural village was sampled from each town.

Procedure

Villagers were invited to provide a fresh stool sample (about 30 g) in a container. Stool samples were transferred to local county-level Center for Disease Control and Prevention (CDC) or Control Station of Parasitic Diseases. From each stool sample, double Kato-Katz thick smears [12], using 41.7 mg templates, were prepared and then examined qualitatively and quantitatively for helminth eggs under a microscope by trained technicians. The preparation of Kato-Katz smears was usually done within 24 hours after samples were collected. Smears were examined within 30 minutes after preparation to avoid the disappearance of hookworm eggs. In each sampled county, 50 individuals with confirmed hookworm infection by the Kato-Katz method were sampled and their stool was further processed to differentiate between the hookworm species by the test-tube filter-paper hatching method [12]. If the number of cases with hookworm infections by the Kato-Katz method was less than 50, they were all included. In brief, 0.5 g of fresh stool were placed on a folded strip of filter paper (9.0 cm in length and 1.6 cm in width), which was then placed in a plastic tube (11.5 cm in length and 1.5 cm in width) containing 2 ml of sterile distilled water and incubated at 30°C for 4–5 days. Then, filariform larvae were taken to differentiate the species by the morphology, especially the differences of the oral spear and transverse lines on the tunica vaginalis [12]. All larvae were differentiated if the total number was below 100 in single sample, while the number exceed 100, only 100 larvae were examined.

Statistical analysis

Individual egg counts, expressed as eggs per gram (EPG) of stool, were calculated by multiplying the sum of the egg counts in the 41.7 mg template used by the two Kato-Katz thick smears by 12. Infection intensity was categorized as per WHO guideline [13]. In hookworm infections, it was categorized as light (1–1999 EPG), moderate (2000–3999 EPG), and heavy (≥ 4000 EPG); in ascariasis, the categories contained light (1–4999 EPG), moderate (5000–49999 EPG), and heavy (≥ 50000 EPG); in trichuriasis, the categories contained light (1–999 EPG), moderate (1000–9999 EPG), and heavy (≥ 10000 EPG). Ages were classified into groups with an interval of 5 years, except those aged over 85 who were considered as a single group. Weighted prevalence was applied. To calculate this, the weight (W) was firstly captured, which was integrated with the base sampling weight (W) and post-sampling adjusted weight (W) as expressed by: where W is the ratio of the total population of the age and gender group divided by the sampled population in the same group. The total rural population figure was extracted from the sixth national population census in 2010. W is the multiplied sampling weights in the three strata as expressed by: where W is the weight in sampling county in each 2nd substratum, W the weight of the sampled town in each sampled county and W the weight of the sampled natural villages of each sampled town. The weighted prevalence, , in the total rural population was calculated based on follows: where w is described by Eq 1, y the result of stool examination of the ith individual and S the sample size. The total population infected, n, was calculated by: Taylor Series Expansion Method was employed to estimate the confidential interval (CI). Data were presented both at the province and ecozone levels, for each species, as well as the overall group of STH. The proportion of two genera of human hookworm, namely Ancylostoma spp. and N. americanus was also presented.

Results

Characteristics of participants

The survey took place between June 2014 and May 2015 and included 484,210 participants in total (238,505 males and 245,705 females) and they came from 1,890 sampling units in 604 counties belonging to 31 provinces. Among the sampled population, 5,423 persons (1.12%) were found to be infected with hookworm, 4,343 (0.90%) with A. lumbricoides, 1,756 (0.36%) with T. trichiura. Overall, 10,681 (2.21%) of them were infected with at least one helminth species.

STH prevalence

A weighted national prevalence of 4.49% (95% CI: 2.45%-6.53%) was demonstrated for STH (Tables and ). STH were detected in all 31 provinces, of which nine exceeded the average. The highest prevalence was found in Sichuan province (23.55%, 95% CI: 12.11%-34.99%), followed by Hainan (12.23%, 95% CI: 9.16%-15.30%) and Guizhou (10.68%, 95% CI: 7.38%-13.97%) ( and ). STH were found in 44 out of 46 ecozones, of which 10 exceed the average. The prevalence was highest in the Sichuan Basin ecozone (22.16%; 95% CI: 10.84%-33.48%), followed by Hainan Central Mountain ecozone (21.92%; 95% CI: 17.52%-26.33%) ( and ). Thus, STH was still highly prevalent (> 5%) in the western regions and moderately so (> 1%) in the eastern and central areas, while the northern areas showed a low prevalence.

Weighted prevalence of soil-transmitted helminthiasis by provinces in China in 2014–2015.

A. Soil-transmitted helminthiasis. B. Hookworm infections. C. Ascariasis. D. Trichuriasis. The base layer is from https://www.webmap.cn/mapDataAction.do?method=forw&resType=5&storeId=2&storeName=%E5%9B%BD%E5%AE%B6%E5%9F%BA%E7%A1%80%E5%9C%B0%E7%90%86%E4%BF%A1%E6%81%AF%E4%B8%AD%E5%BF%83&fileId=BA420C422A254198BAA5ABAB9CAAFBC1 with credit to National Catalogue Service For Geographic Information.

Weighted prevalence of soil-transmitted helminthiasis by ecozones in China in 2014–2015.

A. Soil-transmitted helminthiasis. B. Hookworm infections. C. Ascariasis. D. Trichuriasis. The base layer is from https://www.webmap.cn/mapDataAction.do?method=forw&resType=5&storeId=2&storeName=%E5%9B%BD%E5%AE%B6%E5%9F%BA%E7%A1%80%E5%9C%B0%E7%90%86%E4%BF%A1%E6%81%AF%E4%B8%AD%E5%BF%83&fileId=BA420C422A254198BAA5ABAB9CAAFBC1 with credit to National Catalogue Service For Geographic Information.

Hookworm infections

Hookworm infections had a weighted prevalence of 2.62% (95% CI: 0.86%-4.38%) nationally (Tables and ). Hookworm infections were detected in 19 provinces, of which 10 exceeded the average. The highest prevalence was found in Sichuan province (14.55%, 95% CI: 1.79%-27.30%), followed by Hainan (8.10%, 95% CI: 3.61%-12.59%) ( and ). Hookworm infections were found in 22 out of 46 ecozones, of which nine exceed the average. The highest weighted prevalence was found in Sichuan Basin ecozone (20.34%; 95% CI: 8.27%-32.41%), followed by Hainan Central Mountain ecozone (15.54%; 95% CI: 9.97%-21.10%) ( and ). Overall, hookworm infections were extremely common in the western regions, moderately so in the southern areas, while the northern areas were non-endemic. a 0.0011 (0.0000–0.0032) Out of the overall 5,423 cases with hookworm infections identified by the Kato-Katz method, 3,579 were subjected to species differentiation. Among them, 479 (13.38%) cases were infected with only Ancylostoma species, 2,808 (78.46%) with only N. americanus, while 292 (8.16%) cases were simultaneously infected with both species. At the provincial level, 19 showed infection with at least one hookworm species, and out of the 18 where species differentiation was attempted, five showed only Ancylostoma species infections, two only N. americanus infections, while another 11 had both (). Out of 22 ecozones with hookworm infections, species differentiation was performed on 20. One ecozone was detected with only Ancylostoma species infections, three with only N. americanus infections and 16 ecozones had both hookworm genera (). Overall, Ancylostoma spp. was predominantly endemic in the northern areas, while N. americanus were mainly found in the southern regions.

The proportion of hookworm species in China in 2014–2015.

A. By provinces. B. By ecozones. The base layer is from https://www.webmap.cn/mapDataAction.do?method=forw&resType=5&storeId=2&storeName=%E5%9B%BD%E5%AE%B6%E5%9F%BA%E7%A1%80%E5%9C%B0%E7%90%86%E4%BF%A1%E6%81%AF%E4%B8%AD%E5%BF%83&fileId=BA420C422A254198BAA5ABAB9CAAFBC1 with credit to National Catalogue Service For Geographic Information.

Ascariasis

Ascariasis showed a weighted prevalence of 1.36% (95% CI: 0.49%-2.23%) nationally (Tables and ). Ascariasis were detected in all 31 provinces, out of which nine exceeded the average. The highest prevalence was found in Sichuan province (6.83%, 95% CI: 0.00%-17.45%), followed by Guizhou (6.15%, 95% CI: 3.59%-8.71%) ( and ). Ascariasis was found in 42 of 46 ecozones, out of which 10 exceed the average. The highest weighted prevalence was found in South Western Sichuan—Central Northern Yunnan Mountain ecozone (10.02%; 95% CI: 0.00%-24.57%), followed by Central Guizhou Karst ecozone (5.30%; 95% CI: 3.68%-6.93%) ( and ). Overall, ascariasis was highly prevalent (> 5%) in the western regions but less prevalent in the northern and eastern areas. a 0.0005 (0.0000–0.0016) b 0.0014 (0.0000–0.0043)

Trichuriasis

Trichuriasis demonstrated a weighted prevalence of 1.02% (95% CI: 0.15%-1.89%) nationally (Tables and ). It was detected in 28 provinces, out of which six exceeded the average. The highest prevalence was found in Sichuan province (6.43%, 95% CI: 0.00%-16.75%), followed by Hainan (4.30%, 95% CI: 0.00%-10.25%) and Yunnan (4.18%, 95% CI: 1.37%-6.99%) ( and ). It was found in 32 of 46 ecozones, out of which eight exceed the average. The highest weighted prevalence was found in South Western Sichuan—Central Northern Yunnan Mountain ecozone (10.43%; 95% CI: 0.00%-23.87%), followed by Hainan Central Mountain ecozone (7.95%; 95% CI: 7.57%-8.33%) ( and ). Trichuriasis were highly prevalent in the western regions, moderately so in central areas, but very much less common in the northern areas. a 0.0015 (0.0000–0.0046)

Age and gender distribution

Hookworm infections were highly prevalent in elderly, especially those over 60, who had a prevalence over 6% ( and ). The prevalence of hookworm infections was 2.29% (95% CI: 0.77%-3.81%) and 2.96% (95% CI: 0.93%-4.99%) in males and females, respectively. The difference in prevalence of ascariasis was not significant by age groups. However, a relatively high prevalence was demonstrated in those aged less than 20. The prevalence in age groups 0–4, 5–9, 10–14 and 15–19 was 1.66%, 1.94%, 2.20% and 1.70%, respectively. Additionally, the prevalence of ascariasis was 1.25% (95% CI: 0.46%-2.03%) and 1.48% (95% CI: 0.52%-2.44%) in males and females, respectively. Similarly, although the difference was not significant, the prevalence of trichuriasis was also a little high in those aged 5–19. The prevalence in age groups 5–9, 10–14 and 15–19 was 1.74%, 2.13% and 1.81%, respectively. The prevalence of trichuriasis was 1.06% (95% CI: 0.15%-1.97%) in males and 0.97% (95% CI: 0.14%-1.81%) in females.

Estimated population infected

Overall, 29.12 million (95% CI: 15.88 million-42.32 million) people were estimated to be infected with at least one STH species and eight provinces harboured over 1 million infections; namely Sichuan (12.06 million), Yunnan (2.60 million), Guizhou (2.40 million), Guangdong (2.05 million), Guangxi (1.86 million), Hunan (1.63 million), Jiangxi (1.38 million) and Anhui (1.38 million). 16.97 million (95% CI: 5.57 million-28.39 million) people were estimated to have hookworm infections, among which 15.02 million (88.48%), 0.95 million (5.61%) and 1.00 million (5.91%) had light, moderate and heavy infections, respectively (). Four provinces harboured over 1 million infections, namely Sichuan (7.45 million), Guangdong (1.76 million), Anhui (1.30 million) and Yunnan (1.14 million). The number of people infected with A. lumbricoides was 8.83 million (95% CI: 3.18 million-14.45 million). Two provinces harboured over 1 million cases, namely Sichuan (3.50 million) and Guizhou (1.38 million). Among them, the numbers of light, moderate and heavy infections were 6.15 million (69.66%), 2.10 million (23.80%) and 0.58 million (6.54%), respectively (). About 6.60 million (95% CI: 0.97 million-12.25 million) people were estimated with T. trichiura infection, out of which 5.75 million (87.13%), 0.85 million (12.81%) and 0.04 million (0.05%) were light, moderate and heavy infections, respectively (). Two provinces harboured over 1 million, namely Sichuan (3.29 million) and Yunnan (1.24 million).

Discussion

This national survey updates the epidemiological map of STH in China. The prevalence of STH has decreased from 53.58% in 1988–1992 to 19.56% in 2001–2004 and then to 4.49% in this survey, while the number of estimated population with infection decreased from 646 million to 129 million and finally to 29 million [7,8]. It is thus obvious that significant control on STH has been achieved in rural China. Firstly, it is well established that endemicity of STH is related to poverty and inadequate access to health infrastructure [14,15], which have both improved over the almost 30 years since the first survey. The rate of poverty in rural China (defined as annual income below 2,300 Chinese Yuan) decreased from 73.5% of the population in 1990 to 5.7% in 2015 [16]. The coverage of piped water increased to 79.0% in 2014 [17], while the coverage of households with toilets in rural China increased to 78.4% in 2015, out of which 57.5% had non-hazardous toilets in which pathogens could be killed [17]. Secondly, huge intervention measures have been implemented with respect to control of STH. After the first national survey, such measures were applied in schools including health education, provision of safe water, improvement of sanitation and mass drug administration of needed pharmaceuticals [18]. After the second national survey, the measures in schools mentioned above have been applied in the community in general [19-21]. Although there was a significant decrease in STH infections, an imbalance of distribution is demonstrated due to multi-factorial impact. While the unsuitable natural environment of northern China (e.g. temperature, humidity) is a reason for the low endemicity of STH, especially hookworm infections, economic development has also been a crucial factor which has contributed to the decrease in STH infections [22]. As seen in the rural areas in eastern China, economic development impacts on STH in two ways. First, it reduces overall poverty leading to piped water and improved sanitation, but it also simultaneously promotes the implementation of health interventions. For example, the coverage of water supplement and sanitation is now usually over 90% in the eastern part of the country [17], while the economic development in western China is still lagging resulting in a lower coverage of water supplement and sanitation. Coverage has not yet reached 60% in the three most endemic provinces, namely Sichuan, Guizhou and Yunnan [17]. In this national survey, although the prevalences of ascariasis and trichuriasis were not significantly different by ages, but still a little higher in children. On the one hand, due to the poor hygiene, children are usually highly prevalent with both ascariasis and trichuriasis [4-6]. On the other hand, the overall low prevalence of ascariasis and trichuriasis weakened the difference. However, in western China, there still exist some factors contributing to the relatively high prevalence of ascariasis and trichuriasis in children, e.g. many siblings, low maternal education, low coverage of piped water and sanitation [23]. On the comparison, the prevalence of hookworm infections was significantly higher in adults. Human stool is still used as fertilizer in some remote areas in China and thus adults have more chance to be infected during agricultural activities [24]. Importantly, not only has the overall number of infections declined strongly, the predominance between the diseases has also changed, so that hookworm has changed from being the least common at 17% in 1988–1992 [7] to be the most common at 2.6% in 2014–2015. Ascariasis and trichuriasis are both more prevalent in children [4-6]. It is likely that school-based mass drug administration contributed to this large decrease in cases. Additionally, because of family planning, most families only raise one child, who therefore gets higher attention than of brothers and sister were around [23]. Furthermore, the provision of clean water and improvement in sanitation show higher effectiveness against ascariasis and trichuriasis than hookworm [14]. The composition of Ancylostoma spp., N. americanus and mix infections has changed from 43.17%, 42.20% and 14.63%, respectively, in 1988–1992 to 13.38%, 78.46% and 8.16% in this survey. The frequently used anthelmintic, albendazole, has a higher efficacy against A. duodenale (91.8%) than against N. americanus (75.0%) [25]. However, other factors might also contribute to this change, which deserve to be explored. In this national survey, provinces, ecozones and economic level were included as the strata for the multiple-stage stratified cluster sampling, which increased the representativeness of sampled population. The estimation of sample size was based on the ecozones in each province, and thus this survey not only demonstrates the prevalence at national, provincial, ecozone level, but also at subprovincial (ecozones in each province) level, which would benefit the adoption of targeted strategy in different levels in future. However, there are several limitations in this survey. First, taking into consideration of the relatively low prevalence of STH in China, missed diagnoses cannot be avoided when only two smears from single sample were examined in this survey. Thus, the prevalence and estimated population under infection may be somewhat underestimated. Second, although A. duodenale and N. americanus are believed to be the predominant hookworm species in China, A. ceylanicum has also been reported in southern China [26]. Molecular techniques are needed in this situation, which deserves to be explored in further studies. After all, a One Health (veterinary and medical) approach to hookworm control is required in the areas where A. ceylanicum is found to be a common hookworm. Overall, STH is now at a low endemic level in China. However, further control activities should be implemented in western parts of the country, especially in Sichuan, Yunnan and Guizhou provinces, which harbor over half of the STH cases discovered. Health education should be strengthened both in school and community. The predominance of hookworm infection requires implementation of community-based interventions. Additionally, water supply and improvement of sanitation should be prioritized in these areas. China has been listed among the countries most feasible to achieve the transmission interruption of STH [22,27]. Significantly, the interruption of STH should firstly be attempted in the northern and eastern China, where the prevalence has decreased to less than 1%. China has eliminated poverty in 2020 and established what is called healthy China by 2030, a plan in which the elimination of the STH could be integrated [28].

STROBE (Strengthening The Reporting of OBservational Studies in Epidemiology) Checklist.

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Weighted prevalence and estimated population infected of soil-transmitted helminthiasis by ecozones in China in 2014–2015.

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Weighted prevalence and estimated population infected of hookworm by ecozones in China in 2014–2015.

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Weighted prevalence and estimated population infected of ascariasis by ecozones in China in 2014–2015.

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Weighted prevalence and estimated population infected of trichuriasis by ecozones in China in 2014–2015.

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Weighted prevalence of soil-transmitted helminthiasis by ages and genders in China in 2014–2015.

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Estimated population infected of soil-transmitted helminthiasis by infection intensity and provinces in China in 2014–2015.

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Table 1

Weighted prevalence and estimated population infected of soil-transmitted helminthiasis by provinces in China in 2014–2015.

ProvinceNo. sampledNo. infectedPrevalence (%)Weighted prevalence (%) (95% CI)Estimated population infected
Beijing 13401120.090.05 (0.00–0.13)1419 (0–3446)
Tianjin 1110770.060.03 (0.00–0.07)690 (0–1792)
Hebei 26526190.070.16 (0.00–0.32)63307 (0–128125)
Shanxi 1950030.020.00 (0.00–0.01)801 (0–1828)
Neimenggu 20132230.110.19 (0.02–0.36)19941 (2065–37178)
Liaoning 26520780.290.27 (0.01–0.52)43749 (1637–85144)
Jilin 19683740.380.36 (0.00–0.74)43968 (0–89466)
Heilongjiang 2645630.010.00 (0.00–0.01)462 (0–1549)
Shanghai 13547130.100.04 (0.00–0.11)1025 (0–2653)
Jiangsu 13275350.260.24 (0.14–0.34)74879 (43303–105165)
Zhejiang 199353871.941.38 (0.48–2.27)288066 (100448–475034)
Anhui 123002912.374.48 (0.76–8.20)1377543 (233690–2521397)
Fujian 77212092.711.58 (0.86–2.31)238786 (129614–348148)
Jiangxi 1864912196.545.61 (4.01–7.22)1380461 (986690–1776534)
Shandong 136201000.730.63 (0.00–1.35)301081 (0–648317)
Henan 26866990.370.47 (0.00–1.09)269771 (0–630264)
Hubei 92151181.280.45 (0.09–0.81)122741 (24523–220704)
Hunan 2638911404.324.60 (2.84–6.37)1630143 (1005684–2255707)
Guangdong 93093223.466.37 (1.04–11.70)2051225 (335012–3768882)
Guangxi 57023486.107.07 (4.28–9.85)1862301 (1128112–2596238)
Hainan 269839014.4612.23 (9.16–15.30)523656 (392265–655203)
Chongqing 92506627.167.90 (6.20–9.60)975358 (765461–1185229)
Sichuan 11403148813.0523.55 (12.11–34.99)12057181 (6199625–17912872)
Guizhou 7572112714.8810.68 (7.38–13.97)2400557 (1659200–3140790)
Yunnan 506795018.758.73 (3.38–14.08)2596412 (1004966–4186366)
Xizang 179392681.491.61 (0.17–3.05)33177 (3500–62790)
Shaanxi 199002091.051.57 (0.21–2.94)322025 (42938–601134)
Gansu 174373351.921.62 (0.72–2.52)284791 (126722–443527)
Qinghai 128591381.070.91 (0.43–1.39)27596 (13016–42075)
Ningxia 133463032.271.94 (0.96–2.93)63284 (31255–95393)
Xinjiang 268863111.160.51 (0.10–0.93)61614 (12057–112126)
Total 484210106812.214.49 (2.45–6.53)29118009 (15877565–42318571)
Table 2

Weighted prevalence and estimated population infected of hookworm by provinces in China in 2014–2015.

ProvinceNo. sampledNo. infectedPrevalence (%)Weighted prevalence (%) (95% CI)Estimated population infected (95% CI)
Beijing 1340100.000.000
Tianjin 1110700.000.000
Hebei 2652600.000.000
Shanxi 1950010.010.00 (0.00–0.00)a196 (0–585)
Neimenggu 2013200.000.000
Liaoning 2652000.000.000
Jilin 1968300.000.000
Heilongjiang 2645600.000.000
Shanghai 1354700.000.000
Jiangsu 13275180.140.11 (0.02–0.20)34360 (6186–61862)
Zhejiang 199353571.791.30 (0.45–2.16)272393 (94170–452015)
Anhui 123002592.114.21 (0.62–7.81)1295564 (190642–2401477)
Fujian 77211862.411.45 (0.76–2.14)218171 (114542–322527)
Jiangxi 186499355.013.49 (2.26–4.72)858162 (556089–1161390)
Shandong 1362030.020.01 (0.00–0.03)4362 (0–14407)
Henan 26866280.100.11 (0.00–0.30)62757 (0–173467)
Hubei 9215520.560.06 (0.00–0.19)16485 (0–51770)
Hunan 263897012.662.71 (1.34–4.08)959555 (474513–1444786)
Guangdong 93092252.425.47 (0.48–10.45)1760943 (154621–3366224)
Guangxi 57022093.673.79 (2.90–4.69)999527 (764375–1236178)
Hainan 26982258.348.10 (3.61–12.59)346769 (154594–539150)
Chongqing 92504685.065.67 (3.69–7.66)700516 (455573–945714)
Sichuan 114038117.1114.55 (1.79–27.30)7446876 (916377–13976033)
Guizhou 75724776.303.81 (0.14–7.48)856512 (31475–1681683)
Yunnan 50674579.023.83 (0.66–7.00)1138563 (196236–2081290)
Xizang 1793940.020.02 (0.00–0.04)369 (0–823)
Shaanxi 1990000.000.000
Gansu 1743700.000.000
Qinghai 1285900.000.000
Ningxia 1334670.050.08 (0.00–0.18)2443 (0–5860)
Xinjiang 2688600.000.000
Total 48421054231.122.62 (0.86–4.38)16974524 (5573349–28385198)

a 0.0011 (0.0000–0.0032)

Table 3

Weighted prevalence and estimated population infected of ascariasis by provinces in China in 2014–2015.

ProvinceNo. sampledNo. infectedPrevalence (%)Weighted prevalence (%) (95% CI)Estimated population infected (95% CI)
Beijing 13401120.090.05 (0.00–0.13)1419 (0–3446)
Tianjin 1110770.060.03 (0.00–0.07)690 (0–1792)
Hebei 26526190.070.16 (0.00–0.32)63307 (0–128125)
Shanxi 1950010.010.00 (0.00–0.00)a97 (0–292)
Neimenggu 20132180.090.11 (0.00–0.26)11741 (0–26851)
Liaoning 26520760.290.26 (0.00–0.51)42088 (0–83507)
Jilin 19683720.370.35 (0.00–0.72)42293 (0–87048)
Heilongjiang 2645620.010.00 (0.00–0.00)b222 (0–666)
Shanghai 13547110.080.04 (0.00–0.09)899 (0–2171)
Jiangsu 13275160.120.12 (0.08–0.16)37687 (24745–49490)
Zhejiang 19935130.070.04 (0.00–0.07)7488 (0–14649)
Anhui 12300120.100.06 (0.00–0.12)17698 (0–36898)
Fujian 772140.050.03 (0.00–0.08)5229 (0–12057)
Jiangxi 186491620.871.25 (0.43–2.08)308656 (105805–511799)
Shandong 13620220.160.12 (0.00–0.24)57591 (0–115256)
Henan 26866500.190.21 (0.00–0.50)119778 (0–289112)
Hubei 9215400.430.14 (0.00–0.29)38630 (0–79017)
Hunan 263894281.621.93 (0.96–2.91)685100 (339950–1030472)
Guangdong 9309630.680.81 (0.23–1.38)260207 (74089–444535)
Guangxi 5702761.331.93 (0.94–2.92)508485 (247763–769646)
Hainan 269820.070.02 (0.00–0.07)933 (0–2998)
Chongqing 92502112.282.48 (1.07–3.90)306227 (132104–481499)
Sichuan 114035404.746.83 (0.00–17.45)3495270 (0–8933398)
Guizhou 75726148.116.15 (3.59–8.71)1382450 (807118–1958216)
Yunnan 50673817.522.19 (0.54–3.84)651399 (160557–1141736)
Xizang 179392161.201.35 (0.13–2.58)27885 (2676–53114)
Shaanxi 199002091.051.57 (0.21–2.94)322025 (42938–601134)
Gansu 174373331.911.62 (0.72–2.51)284263 (126722–441767)
Qinghai 128591381.070.91 (0.43–1.39)27596 (13016–42075)
Ningxia 133462892.171.82 (0.82–2.82)59253 (26697–91812)
Xinjiang 268863061.140.49 (0.08–0.91)59566 (9645–109714)
Total 48421043430.901.36 (0.49–2.23)8826171 (3175513–14451824)

a 0.0005 (0.0000–0.0016)

b 0.0014 (0.0000–0.0043)

Table 4

Weighted prevalence and estimated population infected of trichuriasis by provinces in China in 2014–2015.

ProvinceNo. sampledNo. infectedPrevalence (%)Weighted prevalence (%) (95% CI)Estimated population infected
Beijing 1340140.030.02 (0.00–0.05)401 (0–1325)
Tianjin 1110700.000.000
Hebei 2652600.000.000
Shanxi 1950010.010.00 (0.00–0.01)508 (0–1828)
Neimenggu 2013250.020.08 (0.00–0.20)8200 (0–20654)
Liaoning 2652050.020.01 (0.00–0.03)2043 (0–4912)
Jilin 1968320.010.01 (0.00–0.04)1675 (0–4836)
Heilongjiang 2645610.000.00 (0.00–0.00)a239 (0–713)
Shanghai 1354720.010.01 (0.00–0.01)125 (0–241)
Jiangsu 1327520.020.01 (0.00–0.03)3188 (0–9279)
Zhejiang 19935200.100.05 (0.00–0.09)9854 (0–18834)
Anhui 12300230.190.41 (0.01–0.81)126709 (3075–249065)
Fujian 7721210.270.11 (0.02–0.20)16362 (3014–30143)
Jiangxi 186491520.821.11 (0.00–2.36)273581 (0–580695)
Shandong 13620790.580.52 (0.00–1.20)248509 (0–576282)
Henan 26866250.090.15 (0.01–0.30)89485 (5782–173467)
Hubei 9215270.290.25 (0.00–0.55)67744 (0–149861)
Hunan 26389390.150.15 (0.06–0.25)54591 (21247–88529)
Guangdong 9309420.450.25 (0.05–0.46)80957 (16106–148178)
Guangxi 5702841.471.88 (0.17–3.60)496326 (44808–948879)
Hainan 26981726.384.30 (0.00–10.25)184085 (0–438943)
Chongqing 9250210.230.28 (0.03–0.52)33975 (3704–64200)
Sichuan 114033603.166.43 (0.00–16.75)3292254 (0–8575039)
Guizhou 75721632.151.59 (0.78–2.40)357555 (175363–539577)
Yunnan 50674298.474.18 (1.37–6.99)1242831 (407338–2078316)
Xizang 17939570.320.29 (0.00–0.75)6066 (0–15440)
Shaanxi 1990050.030.00 (0.00–0.01)543 (0–2045)
Gansu 1743730.020.00 (0.00–0.01)718 (0–1760)
Qinghai 1285900.000.000
Ningxia 1334670.050.05 (0.00–0.10)1589 (0–3256)
Xinjiang 2688650.020.02 (0.00–0.04)2048 (0–4823)
Total 48421017560.361.02 (0.15–1.89)6602163 (972096–12248407)

a 0.0015 (0.0000–0.0046)

  22 in total

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Authors: 
Journal:  World Health Organ Tech Rep Ser       Date:  2002

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Authors: 
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Journal:  Zhongguo Xue Xi Chong Bing Fang Zhi Za Zhi       Date:  2015-04

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Authors: 
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Authors:  Xiaobing Wang; Linxiu Zhang; Renfu Luo; Guofei Wang; Yingdan Chen; Alexis Medina; Karen Eggleston; Scott Rozelle; D Scott Smith
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Authors:  Kathrin Ziegelbauer; Benjamin Speich; Daniel Mäusezahl; Robert Bos; Jennifer Keiser; Jürg Utzinger
Journal:  PLoS Med       Date:  2012-01-24       Impact factor: 11.069

9.  Canine and feline parasitic zoonoses in China.

Authors:  Jia Chen; Min-Jun Xu; Dong-Hui Zhou; Hui-Qun Song; Chun-Ren Wang; Xing-Quan Zhu
Journal:  Parasit Vectors       Date:  2012-07-28       Impact factor: 3.876

10.  Geographical distribution of soil transmitted helminths and the effects of community type in South Asia and South East Asia - A systematic review.

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