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Revista do Instituto de Medicina Tropical de São Paulo

versión On-line ISSN 1678-9946

Rev. Inst. Med. trop. S. Paulo vol.60  São Paulo  2018  Epub 28-Jun-2018

http://dx.doi.org/10.1590/s1678-9946201860024 

ORIGINAL ARTICLE

Focal persistence of soil-transmitted helminthiases in impoverished areas in the State of Piaui, Northeastern Brazil

Kerla Joeline Lima Monteiro1  *

Elis Regina Chaves dos Reis1  *

Beatriz Coronato Nunes1 

Lauren Hubert Jaeger1 

Deiviane Aparecida Calegar1 

Jéssica Pereira dos Santos2 

Alexander de Oliveira Maia3 

Samanta Cristina das Chagas Xavier4 

Márcio Neves Bóia3 

Filipe Anibal Carvalho-Costa1  2 

1Fundação Oswaldo Cruz, Instituto Oswaldo Cruz, Laboratório de Epidemiologia e Sistemática Molecular, Rio de Janeiro, Rio de Janeiro, Brazil

2Fundação Oswaldo Cruz, Escritório Técnico Regional, Teresina, Piauí, Brazil

3Fundação Oswaldo Cruz, Instituto Oswaldo Cruz, Laboratório de Biologia e Parasitologia de Mamíferos Silvestres Reservatórios, Rio de Janeiro, Rio de Janeiro, Brazil

4Fundação Oswaldo Cruz, Instituto Oswaldo Cruz, Laboratório de Biologia de Tripanosomatídeos, Rio de Janeiro, Rio de Janeiro, Brazil

ABSTRACT

This study aims to describe the prevalence, distribution, and factors associated with soil-transmitted helminthiases (STHs) in rural localities in Piaui, Brazil. Two cross-sectional surveys (n=605 subjects; 172 families) were carried out in order to obtain socio-demographic, anthropometric, spatial and parasitological data. Parasites were evaluated using Kato-Katz and centrifugal sedimentation techniques. Eggs were measured to assess infection with zoonotic Strongylida parasites. Kernel maps were constructed with Q-GIS. The prevalence of hookworm infection was 12.4% (75/605). Other helminthes found were Trichuris trichiura (n=1; 0.2%) and Hymenolepis nana (n=1; 0.2%). The hookworm positivity rate was significantly lower among subjects who had used albendazole when compared with individuals who had not used anthelmintics or had used antiprotozoal drugs in the last 6 months (8/134 [6.0%] vs. 59/415 [14.2%]; p=0.009). A total of 39/172 (22.7%) families had at least one infected member. The association between the number of dwellers and hookworm positivity in the family was present in a logistic regression multivariate model. Assessment of worm burdens showed 92.2% light, 6.2% moderate, and 1.6% heavy infections. Hookworm eggs (n=34) measured 57.2 - 75.4 µm in length and 36.4 - 44.2 µm in width (mean ± SD = 65.86 ± 4.66 µm L and 40.05 ± 1.99 µm W), commensurate with human hookworms. Hotspots suggest that transmission has a focal pattern. STHs persist in impoverished rural areas in Northeastern Brazil where currently available control strategies (mass drug administration) apparently do not allow the elimination of the infection.

Key words: Soil-transmitted helminthiases; Hookworm; Prevalence; Epidemiology; Northeast Brazil

INTRODUCTION

Soil-transmitted helminthiases (STHs) are neglected, poverty-related diseases with higher prevalence in developing countries. These parasites require passage through the soil for the maturation of their infective stages. Among the geohelminths, Ascaris lumbricoides and Trichuris trichiura are transmitted by ingestion of eggs, while the infective larvae of the hookworms actively penetrate the skin of the host. They cause insidious damage to the host, leading to growth and development deficits and micronutrient deficiencies1,2. Global STH prevalence estimates demonstrate that ascariasis is the most common STH, with 819 million infected subjects, followed by trichuriasis with 464 million, and hookworm infection with 438 million3. Moreover, hookworm infection is associated with 3.2 million disability-adjusted life years (DALYs) and iron-deficiency anemia in tropical regions4. The relationship between intestinal helminthiases and malnutrition has been demonstrated. Depending on the worm burden, acute complications occur. Ascariasis is associated with intestinal obstruction, and trichuriasis with rectal prolapse.

In developing countries, the current control strategy for STHs is based on mass drug administration (MDA) in preschool- and school-aged children5. MDA has been successfully performed in high-prevalence countries in Asia, sub-Saharan Africa, and Latin America, leading to a reduction in both the prevalence and worm burden6,7. In Brazil, MDA is implemented in schools, targets children aged 5-14 years and involves the periodic administration of a single oral dose of 400 mg albendazole by teachers in selected high-risk municipalities. In Brazil, virtually all children aged 5-14 years attend schools. In the municipalities not targeted by school-based MDA programs, anthelmintics are freely distributed by the primary health care system often without performing parasitological analyses. However, this policy presents limitations, such as differences in drug effectiveness against distinct parasite species with a possible reduction in drug activity, development of resistance and reinfections8-11.

Considering the hypothesis that STH transmission can persist in impoverished areas despite the implementation of control measures, the purpose of this study was to assess STH prevalence, spatial distribution, and associated risk factors in a predominantly rural area of Piaui State, Northeast Brazil, a region where hygiene, access to clean water, and sanitation are inadequate.

MATERIALS AND METHODS

Ethics statement

This study was approved by the Ethics Research Committee of the Oswaldo Cruz Institute/Oswaldo Cruz Foundation (FIOCRUZ), license Nº CAAE: 12125713.5.0000.5248. Written informed consent was obtained from participants or their guardians (parent/guardians provided written informed consent on behalf of any child participants under the age of 18 years). In addition, assent was obtained from participants aged less than 18 years. All data used in the study were anonymized.

Study area

The study was carried out in the municipality of Nossa Senhora de Nazare (NSN) in Piaui State, located in Northeast Brazil (04° 56’ 24” S and 37° 58’ 33” W) comprising an area of 356,264 km2 (Figure 1) and the population is estimated at 4,556 inhabitants. It is distant from the capital (Teresina) about 140 km and the municipality exhibits a low (0.586) human development index (Brazilian Institute of Geography and Statistics IBGE, census 2010)12. The population of the study region is predominantly rural (rural population=70% [3,193/4,556]) living in close contact with domestic sheep, goats and pigs. The public primary health care system covers the entire local population.

Figure 1 - Geographic location of Nossa Senhora de Nazare in Piaui State and aspect of two visited houses 

Study design, sampling strategy, and characteristics of sampled population

A cross-sectional survey (27 localities; 172 families/houses; n=605 subjects) was carried out in two steps, the first from August to September 2014 (n=298; 81 families/houses, dry season) and the second from May to July 2015 (n=307; 91 families/houses, rainy season) (Figure 2). In each year, the sampling strategy was designed to include all families with children of the selected localities within the municipality. The localities were selected based on the possibility of access by car, since some are geographically isolated. The number of localities corresponds to 1/3 of the total number in the municipality. This way, in each year we were able to include around 6.5% of the municipality population. Age distribution of the sampled population was as follows: 0 – 14 years, n=217 (35.9%); 15 – 21 years, n=70 (11.6%); 22 – 45 years, n=180 (29.7%); 46 – 60 years, n=75 (12.4%); > 60 years, n=54 (8.9%); unknown age, n=9 (1.5%). Concerning sex, 327/605 (54%) were female. From the sampled population, 134 subjects (22.1%) had used albendazole and 54 (8.9%) had used mebendazole in the last six months. With respect to education, from 373 adults, 77 (20.6%) were illiterate, 226 (60.6%) had up to four years of education, and 70 (18.8%) had five or more years of education. From 172 families, 107 (62.2%) performed open defecation, 27 (15.7%) lived in houses with uncoated clay floor and 38 (22.1%) were extremely poor (monthly per capita familiar income less than 1 USD). The studied municipality is not included in Brazilian MDA programs.

Figure 2 Flowchart depicting sample size and main results of the cross-sectional surveys performed in Nossa Senhora de Nazare, State of Piaui, Brazil. Legenda: EPG: eggs per gram of feces; HAZ: height-for-age z-scores; WHZ: weight-for-height z-scores; WAZ: weight-for-age z scores 

Members of the research team visited the houses in order to distribute plastic bottles without preservatives for the collection of fecal samples and to gather socio-demographic, anthropometric and sanitation data through face-to-face interviews. Fecal samples where recovered 24 h or 48 h after the bottles were distributed, in a second visit and third visit, if necessary. After the study, the research team conducted health education practices, which involved health care (prevention and correct drug administration measures) and talks for schools (data not shown).

Anthropometric measurements

In order to estimate the impact of STHs on the physical development of children, weight and height measurements were obtained from individuals aged up to 14 years. Weight was measured to the nearest 0.1 kilogram using a digital floor scale. Standing height was measured with a steel measuring tape coupled to a steel framing square. Standard deviation scores (Z-scores) (height-for-age [HAZ], weight-for-height [WHZ], and weight-for-age [WAZ]) were calculated using the NutStat module in Epi InfoTM 2000 (Centers for Disease Control and Prevention [CDC], Atlanta, USA) and the World Health Organization (WHO) growth chart13. Stunting (chronic malnutrition), wasting (acute malnutrition), and underweight (undefined malnutrition) were defined by HAZ, WHZ, and WAZ < -2, respectively, in the reference population14.

Laboratory procedures

Parasitological examinations were performed by the formalin-ethyl acetate centrifugation method (modified Ritchie technique) and the quantitative Kato-Katz thick smear technique (Helm Test® kit, LabHouse, Belo Horizonte, Minas Gerais, Brazil)15,16. The parasitic load was estimated using the Kato-Katz technique (eggs per gram - epg of feces). The hookworm infection intensity was classified into light (1–1,999 epg), moderate (2,000–3,999 epg), or heavy (≥4,000 epg)17. The sucrose spontaneous flotation technique was performed for hookworm-positive individuals in order to facilitate egg measurement. An ocular micrometer was used to measure the eggs. These measures were used to aid the differentiation and provide initial information about the possibility of infection with the zoonotic Strongylida Trichostrongylus sp. As reference measures, we used the following: i) 63-80 µm × 35-49 µm for Necator americanus, ii) 60-77 µm × 35-45 µm for Ancylostoma duodenale, and iii) 75-95 µm × 40-50 µm for Trichostrongylus sp.18,19. The R program v.3.2.3 was used for the descriptive statistics of egg measurements.

The results of the parasitological examinations were delivered to each study participant, and a treatment was performed with a 3-day course of mebendazole (100 mg twice a day) for STHs.

Spatial analyses

The base map was acquired from IBGE (Brazilian Institute of Geography and Statistics). The coordinates of the sampling sites were determined using a hand-held Global Positioning System (GPS) receiver and were recorded in the SAD 69 datum (South American Datum 1969) geodetic coordinate system. For exploration and modeling, the maps were analyzed for spatial point patterns using the Kernel method. A quartic analysis method was used to allow spatial variation in the point densities, evaluating only the first-order effects. The spatial data were analyzed in a (Geographic Information System) (GIS) platform using the open-source (Quantum GIS) QGIS (version 2.14.3 Essen) a free and open source geographic information system software.

Statistical analyses

Two distinct analytic approaches were performed. At the individual level, we compared the positivity rates by season, by anthelmintic use, and by sex with Fisher’s exact test. Positivity in distinct educational levels and age groups were compared with chi-square test for linear trend. The frequencies of distinct forms of malnutrition (i.e. acute, undefined or chronic, see description below) were compared in the hookworm-positive and hookworm-negative groups of children with Fisher’s exact test. At the family level, positivity rates (i.e. at least one positive person in the house) by site of defecation, type of floor, number of inhabitants, presence of extreme poverty, and presence of pigs, goats, sheep and type of soil were compared with Fisher’s exact test. A multivariate analysis was performed through logistic regression. In the multiple logistic regression model, the outcome was hookworm positivity. The predictors, assessed simultaneously, were season, number of dwellers living in the domicile, type of floor, type of soil, site of defecation, presence of extreme poverty, and presence of goats, pigs and sheep in the peridomicile. The correlation between the intensity of infection (eggs per gram [epg] of feces) and age was assessed through partial correlation, assessing the Spearman’s (Rho) coefficient and its statistical significance. Comparison of egg counts in the rainy and dry seasons were performed with the Kruskall-Wallis test). For all analyses, alpha-level was set at 5% (p<0.05). Statistical analyses were performed with SPSS® (IBM Corp., Armonk, NY, USA).

RESULTS

The overall prevalence of hookworm infection was 12.4% (75/605). There was no infection by Ascaris lumbricoides. Other helminth infections were found to a lesser extent: Trichuris trichiura (n=1; 0.16%) and Hymenolepis nana (n=1; 0.16%). The prevalence rates of hookworm infection in the dry (2014) and rainy (2015) seasons were 11.7% (35/298) and 13% (40/307), respectively (p=0.631) (Table 1). Prevalence reached 12.1% and 14.8% among preschool (0 - 5 years-old) and school (6 - 14 years-old) aged children and positivity rates were similar in distinct age groups (Table 1). The positivity rate was similar among males (40/278 [14.4%]) and females (35/327 [10.7%]), p=0.170. In addition, hookworm positivity was not significantly different among adults with less than four study years (illiterate 11/77 [14.3%] and 1-4 study years 31/226 [13.7%] vs. > 4 study years 3/70 [4.3%]; p=0.052; Table 1). The use of antiparasitic drugs up to 6 months prior to this study was evaluated: 188 (31.07%) subjects used anthelmintic drugs (134 [22.14%] used albendazole and 54 [8.9%] used mebendazole), and 267 (44.3%) subjects used antiprotozoal drugs (252 [41.7%] used metronidazole and 15 [2.5%] used secnidazole). The hookworm positivity rate was significantly lower among subjects who had used albendazole when compared with individuals who had not used anthelmintics or had used antiprotozoal drugs in the last 6 months (8/134 [6.0%] vs. 59/415 [14.2%]; p=0.009). Positivity rates in subjects previously treated with mebendazole were not significantly different from those of individuals treated with albendazole (p=0.078).

Table 1 Hookworm positivity rates in distinct age groups, genders and seasons in Nossa Senhora de Nazare, State of Piaui, Brazil, 2014-2015 

Hookworm positivity rate p-value
Season
Dry 11.7% (35/298) 0.631
Rainy 13% (40/307)
Age in years*
0-5 12.1% (11/91) 0.144
6-14 14.8% (22/149)
15-21 19.2% (9/47)
22-45 10.6% (19/180)
46-60 12.0% (9/75)
> 60 7.4% (4/54)
Unknown 11.1% (1/9)
Use of antihelmintics in the last 6 months**
Albendazole 6.0% (8/134) 0.009
Mebendazole 14.8% (8/54)
None or only antiprotozoal drugs 14.2% (59/415)
Unknown 0.0% (0/2)
Sex
Male 14.4% (40/278) 0.170
Female 10.7% (35/327)
Education in adults
Illiterate 14.3% (11/77) 0.052
1-4 study years 13.7% (31/226)
> 4 study years 4.3% (3/70)

*Chi-square for linear trend **Albendazole vs. none or only antiprotozoal drugs

Considering hookworm positivity in the family, a total of 39/172 (22.7%) families had at least one infected member (Table 2). In the univariate analyses, houses with more than four subjects presented higher hookworm positivity when compared to houses with four or less inhabitants. In addition, positivity in families living in houses with an uncoated clay floor and in those families possessing sheep was significantly higher. Positivity was similar in houses situated in sandy and clayey soil (Table 2). The association between the number of dwellers and hookworm positivity in the family was also present in the logistic regression multivariate model (Table 2).

Table 2 Hookworm positivity rates by family (at least one positive subject in the house) in distinct sociodemographic settings in Nossa Senhora de Nazare, State of Piaui, Brazil, 2014-2015 

Characteristic Hookworm Positivity Crude Odds ratio (95% CI) p-value Adjusted Odds ratio (95% CI) p-value
Season
Dry 16/91 (17.6%) 1.85 (0.90-3.83) 0.065 1.57 (0.70-3.48) 0.267
Rainy 23/81 (28.4%)
Number of dwellers
≤ 4 15/103 (14.6%) 0.31 (0.15-0.66) 0.001 0.29 (0.13-0.67) 0.003
> 4 24/69 (34.8%)
Type of floor
Uncoated floor 11/27 (40.7%) 2.87 (1.20-6.86) 0.017 1.43 (0.52-3.97) 0.480
Ceramic – coated floor 28/145 (19.3%)
Type of soil
Sandy 29/127 (22,8%) 1.03 (0.45-2.34) 0.555 1.23 (0.40-3.71) 0.716
Clayey 10/45 (22,2%)
Site of defecation
Open defecation 22/91 (24.2%) 1.20 (0.58-2.46) 0.376 1.03 (0.39-2.69) 0.938
Latrine 17/81 (21%)
Extreme poverty*
Yes 8/38 (21.1%) 0.89 (0.37-2.16) 0.501 0.73 (0.27-2.00) 0.551
No 30/131 (22.9%)
Presence of goats
Yes 7/34 (20.6%) 0.85% (0.34-20.15) 0.472 1.61(0.52-4.95) 0.402
No 32/138 (26.2%)
Presence of pigs
Yes 23/104 (22.1%) 0.92 (0.44-1.90) 0.485 0.85 (0.36-2.01) 0.723
No 16/68 (23.5%)
Presence of sheep
Yes 0/21 (0%) Undefined 0.003 Undefined 0.962
No 39/151 (25.8%)

* Per capita monthly familiar income < RS$ 70; missing information for one family

In 85.3% (64/75) of hookworm-positive individuals, the infection intensity could be assessed: 59 (92.2%) had light, 4 (6.2%) had moderate and 1 (1.6%) had heavy hookworm infection intensity. Partial correlation analysis showed higher fecal egg counts in younger subjects, but this was not statistically significant (Rho=-0.202; p=0.101) (Figure 3). The median parasite load was similar in the dry and rainy seasons (288 epg [interquartile range = 72 – 912 epg] vs. 168 epg [48 – 312 epg], p = 0.211).

Figure 3 - Scatter plot depicting hookworm egg fecal counts per gram of feces by age 

Hookworm eggs (n=34) measured 57.2 - 75.4 µm in length and 36.4 - 44.2 µm in width (mean ± SD = 65.86 ± 4.66 µm L and 40.05 ± 1.99 µm W), commensurate with human hookworm (Figure 4A and B).

Figure 4 - Boxplots of length (A) and width (B) of hookworm eggs 

It was observed that 60% of the positive subjects were situated in only 2 of the 27 studied localities (Sao Paulo and Passa Bem) and therefore the spatial distribution of hookworm infection presented a focal pattern. The Kernel density map identified six hotspot areas in the municipality of NSN (Figure 5), representing higher transmission areas that present hookworm prevalence ≥ 20%.

Figure 5 - Mapping on the distribution of hookworm infection (municipalities) depicting hotspots (Kernel density) 

The frequencies of distinct forms of malnutrition were not significantly distinct among hookworm-positive and hookworm-negative subjects (not shown). Nevertheless, the frequency of stunting in hookworm-infected children (4/30 [13.3%]) was almost twice the frequency observed in hookworm-negative children (13/181 [7.2%]), but this was not statistically significant (p=0.207). The proportions of underweight hookworm-positive and hookworm-negative children were 3/31 (9.7%) and 24/191 (12.6%), respectively (p=0.458). The frequency of wasting was 0/21 in hookworm-positive and 4/139 (2.8%) in hookworm-negative subjects (p=0.574).

DISCUSSION

Our results demonstrate a moderate prevalence of hookworm infection in NSN, Piaui State, Brazil. According to the WHO and the Brazilian Ministry of Health, regions with an STH prevalence above 20% are considered to be at higher risk and are included in the MDA programs20. The prevalence of STHs in different Brazilian municipalities is largely unknown, and adherence to the MS-funded MDA program is an option of local health authorities. The municipality studied has chosen not to join the MDA program21. Retrospective data analyses have estimated that the prevalence of hookworm infection in Brazil has undergone a drastic decrease in the past 20 years, with expected prevalence rates of 1.7%22 and 2.5%23. A previous work has shown a prevalence of 9.7% in a semiarid region in the state of Piaui in 2000 and 200124.

The sociodemographic and environmental determinants of STHs involve interactions between the physical environment (either natural or man-modified) and human behavior25. We did not observe a higher positivity of hookworm infection in families that performed open defecation compared to families using latrines (septic tanks). The association between open defecation - a common practice among rural populations - and hookworm infection has been described in other developing countries26,27. Interestingly, in our study, open defecation is performed even in dwellings that have a latrine. This suggests that open defecation is, at least in part, culturally determined and not only a consequence of poverty and lack of access to sanitary resources. Children are likely more exposed to infective free-living larvae and tended to present the highest parasite load. In the present study, another risk factor associated with hookworm infection was living in houses with an uncoated clay floor. Despite we did not identify an association between open defecation and hookworm infection at the family level, the high proportion of open defecation in the studied localities can contribute to the circulation of hookworms. In Nairobi and countries in West Africa, open defecation is intrinsically associated with hookworm infection28,29. This sociodemographic scenario enables the persistence of free-living populations of larvae in the peridomestic environment and creates a favorable environment for perpetuating the biological cycle of hookworm and reinfection30. In addition, it was observed that hookworm positivity is significantly associated with overcrowding and lower educational status.

In the studied area, the sociodemographic and environmental scenarios favorable to transmission seems to be spatially concentrated, which could explain the focal pattern of spatial distribution of hookworm infection. The majority of hookworm-positive individuals were found to inhabit only a few localities. This suggests that a spatially targeted approach for hookworm interventions, including hookworm surveys, should be prioritized in high-risk areas.

We observed that hookworm infection was homogenously distributed among different age groups pointing to the necessity of expanding the program for adults, as has been discussed in some studies, providing an effective control measure to interrupt transmission31,32. No statistically significant associations were observed between stunting, wasting, or underweight and hookworm infection in children. As expected, the prevalence of hookworm infection in individuals who used albendazole (up to 6 months prior to the analysis) proved to be significantly lower. In NSN, the public health service provides free antiparasitic drugs for the treatment of STHs. The treatment regimen used is usually a single 400 mg albendazole dose, although resistance to this drug is already considered a problem and its efficacy against different STH species is variable33,34.

Human infection with the zoonotic nematode Trichostrongylus sp. has been described in Brazil and other countries, especially in rural areas and in populations living in close contact with sheep and goats35-37. Although there is little overlap in the length and width measurements, the eggs found in this study were attributable to hookworms. A morphologic study of larvae obtained in coprocultures in addition to the use of molecular taxonomic tools is needed in order to definitively rule out the possibility of misidentifications and infections with zoonotic Strongylida such as Trichostrongylus sp.

Currently, there is a consensus concerning a reduction in the STH burden in developing countries, including Brazil22,38. Our results are in agreement with this proposal, with the exception of hookworm infection. We observed the absence of A. lumbricoides infection and scarce T. trichiura infections in NSN. The reduction in transmission of orally ingested STHs can be partially related to improvements in drinking water supplies and efficient primary health services. On the other hand, the persistence of open defecation and inadequate solid excreta elimination can favor the transmission of skin-penetrating STHs, such as hookworm39. The results can be generalized to small rural communities in the Brazilian semiarid region with similar socio-environmental characteristics and point to the need of current policies improvements for STH control in economically impoverished rural regions of Brazil.

ACKNOWLEDGMENTS

We thank the administrative staff and Primary Health Care Agents of Nossa Senhora de Nazare for support in field activities. We also thank to Dr. Arnaldo Maldonado Junior for providing the ocular micrometer and Ricardo Avancini Fernandes for his support with the Geographic Information System.

REFERENCES

1. Kassebaum NJ, Jasrasaria R, Naghavi M, Wulf SK, Johns N, Lozano R, et al. A systematic analysis of global anemia burden from 1990 to 2010. Blood. 2014;123: 615-24. [ Links ]

2. de Gier B, Nga TT, Winichagoon P, Dijkhuizen MA, van de Bor M, Ponce MC, et al. Species-specific associations between soil-transmitted helminths and micronutrients in Vietnamese schoolchildren. Am J Trop Med Hyg. 2016;95:77-82. [ Links ]

3. Pullan RL, Smith JL, Jasrasaria R, Brooker SJ. Global numbers of infection and disease burden of soil transmitted helminth infections in 2010. Parasit Vectors. 2014;7:37. [ Links ]

4. Murray CJ, Vos T, Lozano R, Naghavi M, Flaxman AD, Michaud C, et al. Disability-adjusted life years (DALYs) for 291 diseases and injuries in 21 regions, 1990-2010: a systematic analysis for the Global Burden of Disease Study 2010. Lancet. 2012;380: 2197-223. [ Links ]

5. World Health Organization. Preventive chemotherapy in human helminthiasis: coordinated use of anthelminthic drugs in control interventions: a manual for health professionals and programme managers. Geneva: WHO; 2006. Available from: http://www.who.int/neglected_diseases/preventive_chemotherapy/pct_manual/en/Links ]

6. Bill & Melinda Gates Foundation. Private and public partners unite to combat 10 neglected tropical diseases by 2020. [cited 2018 Mar 28]. Available from: http://www.gatesfoundation.org/media-center/press-releases/2012/01/private-and-public-partners-unite-to-combat-10-neglected-tropical-diseases-by-2020Links ]

7. World Health Organization. Soil-transmitted helminthiases: eliminating soil-transmitted helminthiases as a public health problem in children: progress report 2001–2010 and strategic plan 2011–2020. Geneva: WHO; 2012. [cited 2018 Mar 28]. Available from: http://apps.who.int/iris/bitstream/10665/44804/1/9789241503129_eng.pdfLinks ]

8. Albonico M, Bickle Q, Ramsan M, Montresor A, Savioli L, Taylor M. Efficacy of mebendazole and levamisole alone or in combination against intestinal nematode infections after repeated targeted mebendazole treatment in Zanzibar. Bull World Health Organ. 2003;81:343-52. [ Links ]

9. Anderson R, Truscott J, Hollingsworth TD. The coverage and frequency of mass drug administration required to eliminate persistent transmission of soil-transmitted helminths. Philos Trans R Soc Lond B Biol Sci. 2014;369:20130435. [ Links ]

10. Turner HC, Truscott JE, Bettis AA, Shuford KV, Dunn JC, Hollingsworth TD, et al. An economic evaluation of expanding hookworm control strategies to target the whole community. Parasit Vectors. 2015;8:570. [ Links ]

11. Webster JP, Molyneux DH, Hotez PJ, Fenwick A. The contribution of mass drug administration to global health: past, present and future. Philos Trans R Soc Lond B Biol Sci. 2014;369:20130434. [ Links ]

12. Instituto Brasileiro de Geografia e Estatística. Brasil/Piauí/Nossa Senhora de Nazaré. [cited 2018 Apr 23]. Available from: https://cidades.ibge.gov.br/brasil/pi/nossa-senhora-de-nazare/panoramaLinks ]

13. World Health Organization. A growth chart for international use in maternal and child health care: guidelines for primary health care personnel. Geneva: WHO; 1978. [cited 2018 Mar 28]. Available from: http://apps.who.int/iris/bitstream/10665/37294/1/9241541296.pdfLinks ]

14. Waterlow JC, Buzina R, Keller W, Lane JM, Nichaman MZ, Tanner JM. The presentation and use of height and weight data for comparing the nutritional status of groups of children under the age of 10 years. Bull World Health Organ. 1977;55:489-98. [ Links ]

15. Katz N, Chaves A, Pellegrino J. A simple device for quantitative stool thick-smear technique in Schistosomiasis mansoni. Rev Inst Med Trop Sao Paulo. 1972;14:397-400. [ Links ]

16. Young KH, Bullock SL, Melvin DM, Spruill CL. Ethyl acetate as a substitute for diethyl ether in the formalin-ether sedimentation technique. J Clin Microbiol. 1979;10:852-3. [ Links ]

17. Pan American Health Organization. World Health Organization. Operational guidelines for the implementation of integrated deworming activities a contribution to the control of soil-transmitted helminth infections in Latin America and the Caribbean. Washington: PAHO/WHO; 2015. [cited 2018 Mar 28]. Available from: http://iris.paho.org/xmlui/bitstream/handle/123456789/31345/9789275118610-eng.pdf?sequence=1&isAllowed=yLinks ]

18. Brumpt E. Précis de parasitologie. 6ème ed. Paris: Masson; 1949. [ Links ]

19. Goldsmid JM. The differentiation of Ternidens deminutus and hookworm ova in human infections. Trans R Soc Trop Med Hyg. 1968;62:109-16. [ Links ]

20. World Health Organization. Helminth control in school age children: a guide for managers of control programmes. 2nd ed. Geneva: WHO; 2011. [cited 2018 Mar 28]. Available from: http://apps.who.int/iris/bitstream/10665/44671/1/9789241548267_eng.pdfLinks ]

21. Brasil. Ministério da Saúde. Secretaria de Vigilância em Saúde. Departamento de Vigilância em Doenças Transmissíveis. Plano integrado de ações estratégicas de eliminação da hanseníase, filariose, esquistossomose e oncocercose como problema de saúde pública, tracoma como causa de cegueira e controle das geo-helmintíases: plano de ação 2011-2015. Brasília: Ministério da Saúde; 2012. [cited 2018 Mar 28]. Available from: http://bvsms.saude.gov.br/bvs/publicacoes/plano_integrado_acoes_estrategicas_2011_2015.pdfLinks ]

22. Chammartin F, Guimarães LH, Scholte RG, Bavia ME, Utzinger J, Vounatsou P. Spatio-temporal distribution of soil-transmitted helminth infections in Brazil. Parasit Vectors. 2014;7:440. [ Links ]

23. Scholte RG, Schur N, Bavia ME, Carvalho EM, Chammartin F, Utzinger J, et al. Spatial analysis and risk mapping of soil-transmitted helminth infections in Brazil, using Bayesian geostatistical models. Geospat Health. 2013;8:97-110. [ Links ]

24. Alves JR, Macedo HW, Ramos Jr NA, Ferreira LF, Gonçalves ML, Araújo A. Parasitoses intestinais em região semi-árida do Nordeste do Brasil: resultados preliminares distintos das prevalências esperadas. Cad Saude Publica. 2003;19:667-70. [ Links ]

25. Confalonieri UE, Margonari C, Quintão AF. Environmental change and the dynamics of parasitic diseases in the Amazon. Acta Trop. 2014;129:33-41. [ Links ]

26. Anuar TS, Salleh FM, Moktar N. Soil-transmitted helminth infections and associated risk factors in three Orang Asli tribes in Peninsular Malaysia. Sci Rep. 2014;4:4101. [ Links ]

27. Schmidlin T, Hürlimann E, Silué KD, Yapi RB, Houngbedji C, Kouadio BA, et al. Effects of hygiene and defecation behavior on helminths and intestinal protozoa infections in Taabo, Côte d’Ivoire. PLoS One. 2013;8:e65722. [ Links ]

28. Soares Magalhães RJ, Barnett AG, Clements AC. Geographical analysis of the role of water supply and sanitation in the risk of helminth infections of children in West Africa. Proc Natl Acad Sci U S A. 2011;108:20084-9. [ Links ]

29. Worrell CM, Wiegand RE, Davis SM, Odero KO, Blackstock A, Cuéllar VM, et al. A cross-sectional study of water, sanitation, and hygiene-related risk factors for soil-transmitted helminth infection in urban school- and preschool-aged children in Kibera, Nairobi. PLoS One. 2016;11:e0150744. [ Links ]

30. Loukas A, Hotez PJ, Diemert D, Yazdanbakhsh M, McCarthy JS, Correa-Oliveira R, et al. Hookworm infection. Nat Rev Dis Primers. 2016:2:16088. [ Links ]

31. Anderson RM, Turner HC, Truscott JE, Hollingsworth TD, Brooker SJ. Should the goal for the treatment of soil transmitted helminth (STH) infections be changed from morbidity control in children to community-wide transmission elimination? PLoS Negl Trop Dis. 2015;9:e0003897. [ Links ]

32. Bartsch SM, Hotez PJ, Asti L, Zapf KM, Bottazzi ME, Diemert DJ, et al. The global economic and health burden of human hookworm infection. PLoS Negl Trop Dis. 2016;10:e0004922. [ Links ]

33. Prichard RK. Markers for benzimidazole resistance in human parasitic nematodes? Parasitology. 2017;134:1087-92. [ Links ]

34. Vercruysse J, Albonico M, Behnke JM, Kotze AC, Prichard RK, McCarthy JS, et al. Is anthelmintic resistance a concern for the control of human soil-transmitted helminths? Int J Parasitol Drugs Drug Resist. 2011;1:14-27. [ Links ]

35. Fleury GC, Corrêa MO, Amato Neto A. Identificação do Trichostrongylus colubriformis como parasita do homem. Rev Inst Med Trop Sao Paulo. 1970;12:288-92. [ Links ]

36. Souza RP, Souza JN, Menezes JF, Alcântara LM, Soares NM, Aquino Teixeira MC, et al. Human infection by Trichostrongylus spp. in residents of urban areas of Salvador city, Bahia, Brazil. Biomedica. 2013;33:439-45. [ Links ]

37. Wall EC, Bhatnagar N, Watson J, Doherty T. An unusual case of hypereosinophilia and abdominal pain: an outbreak of Trichostrongylus imported from New Zealand. J Travel Med. 2011;18:59-60. [ Links ]

38. Brooker SJ, Nikolay B, Balabanova D, Pullan RL. Global feasibility assessment of interrupting the transmission of soil-transmitted helminths: a statistical modelling study. Lancet Infect Dis. 2015;15:941-50. [ Links ]

39. Echazú A, Bonanno D, Juarez M, Cajal SP, Heredia V, Caropresi S, et al. Effect of poor access to water and sanitation as risk factors for soil-transmitted helminth infection: selectiveness by the infective route. PLoS Negl Trop Dis. 2015;9:e0004111. [ Links ]

Recibido: 7 de Diciembre de 2017; Aprobado: 28 de Marzo de 2018

Correspondence to: Kerla Joeline Lima Monteiro Fundação Oswaldo Cruz, Instituto Oswaldo Cruz, Laboratório de Epidemiologia e Sistemática Molecular, Pavilhão Leônidas Deane, sala 308, Avenida Brasil, 4365, CEP 21040-900, Rio de Janeiro, RJ, Brazil Tel: +55 21 3865-8182 E-mail:kerla@ioc.fiocruz.br

AUTHORS’ CONTRIBUTION

Conceived and designed the experiments: KJLM, ERCR, BCN, MNB, and FACC. Performed the experiments: KJLM, BCN, JPS, DAC, and AOM. Analyzed the data: KJLM, LHJ, BCN, SCCX, and FACC. Contributed reagents/materials/analysis tools: ERCR, LHJ, SCCX, MNB. Wrote the paper: KJLM, LHJ, BCN, FACC.

*

This authors contributed equally to this work

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