Transactions of the Royal Society of Tropical
Medicine and Hygiene (2008) 102, 374—379
Parasite contamination of soil in households of a Mexican rural community
endemic for neurocysticercosis
M. Huerta a,c, R. Avila b, H.I. Jim´nez b, R. D´ a, J. D´ c, M.E. D´ Huerta a,
e A±az A±az A±az d e f a,c o M. Hern´ndez , J.J. Martinez , T. Garate , E.
G´mez , T. Abad a, a d g d, G. Fragoso , A.
Fleury , E. Sciutto
a
Facultad de Medicina, Benem´rita Universidad Aut´noma de Puebla, 13 Sur No.
2702, e o Col. Volcanes, Puebla, Pue. Mexico b Escuela de Medicina Veterinaria
y Zootecnia, Benem´rita Universidad Aut´noma de Puebla, 13 Sur No. 2702, e o
Col. Volcanes, Puebla, Pue. Mexico c Unidad Medico Familiar 57 IMSS, Puebla,
Mexico d Instituto de Investigaciones Biom´dicas, Universidad Nacional Aut´noma
de M´xico, Apartado 70228, e o e 04510 M´xico D.F., Mexico e e Facultad de
Medicina Veterinaria y Zootecnia, Universidad Nacional Aut´noma de M´xico, o e
Circuito Escolar Exterior s/n, 04510 M´xico D.F., Mexico e f Ministerio de
Sanidad y Consumo, Instituto de Salud Carlos III, Crta. Majadahonda-Pozuelo Km 2,
28220 Majadahonda, Madrid, Spain g Instituto Nacional de Neurolog´ y
Neurocirug´ Insurgentes Sur 3877, Col. A Fama, Delegaci´n Tlalpan, A±a A±a, o
14269 M´xico D.F., Mexico e Received 2 July 2006; received in revised form 21
December 2007;accepted 21 December 2007
KEYWORDS
Neurocysticercosis; Taenia; Parasitic diseases; Soil microbiology; Rural
communities; Mexico
Summary High neurocysticercosis (NC) prevalence was recently determined by a
computed tomography (CT) scan study in the community of Tepetzitzintla, State
of Puebla, Mexico. The aim of the present work was to evaluate the magnitude of
fecal and parasite contamination by Taenia spp. in the soil of households of
this community during the four seasons of the year. The toilet, backyard,
kitchen, washboard, water containers and corrals of 14 to 26 households were
sampled during each season. High Taenia spp. egg intensity was found in 24.2%
of the sampled areas. The highest percentage was detected in Spring
and the lowest in Summer. Signiï¬cantly higher levels of Taenia
spp. eggs were present in kitchen soil samples. A signiï¬cant correlation was found between the presence of Taenia spp.
eggs in household soil during the Summer, and NC
diagnoses of the inhabitants by CT scan. Coproparasitological examinations and
anticysticercal antibodies were determined in a cohort of inhabitants of the
sampled households. Antibody levels and coproparasitological results were not
associated with NC. Overall, these
∗
Corresponding author. Tel.: +52 55 5622 3153; fax: +52 55 5622 3369.
E-mail address: edda@servidor.unam.mx (E. Sciutto
0035-9203/$ — see front matter © 2008 Royal Society of Tropical Medicine
andHygiene. Published by Elsevier Ltd. All rights
reserved. doi:10.1016/j.trstmh.2007.12.009
Parasite contamination of soil in Mexican households
375
results illustrate the high degree of fecal contamination of potential risk to
human health in rural communities and could be of use for control programmes. © 2008 Royal Society of Tropical Medicine and Hygiene. Published by Elsevier Ltd. All rights reserved.
1. Introduction
In Mexico,
as in other endemic countries, soil contamination with Taenia solium eggs is of
special interest considering the high prevalence of pig and human cysticercosis
reported in rural communities, and the great impact of this disease on human
health. Taenia solium eggs are deposited in the environment through defecation
by humans, the only known deï¬nitive hosts. Human
infection with T. solium occurs by accidental ingestion of eggs in soil, contaminated
vegetables, water, etc. In two independent computed tomography (CT) scan
epidemiological studies performed in two endemic rural communities, 9.1% of
asymptomatic neurocysticercosis (NC) cases were detected (Fleury et al., 2003,
2006). No exposure or socio-economic factors were found to be associated with
the infection. Considering this, the present study evaluated the relationship
between parasite contamination of the soil and the presence of NC and included
identiï¬cation of Taenia spp. eggs in the soil
samples to determine the usefulness of thistechnique for epidemiological
purposes.
2. Materials and methods
2.1. Study area
This study was performed in the rural community of Tepetzitzintla, Puebla,
Mexico, with
1782 inhabitants. The community, located in a region called mixteca poblana,
was selected because of the poor prevailing sanitary and socioeconomic
conditions that promote the life cycle of T. solium (open-air defecation,
absence of toilets and drainage, poor hygienic and dietary habits, rustically
bred pigs, consumption of meat without inspection). Most of the houses have
soil floors, and water is provided only twice a week. In each of the 26 houses
tested, soil samples were taken from the outhouse (a place on the patio used
for defecation over the floor), the backyard (open patio between the areas
most commonly used for speciï¬c purposes, in which
the children and animals dwell), the kitchen (a barely roofed shack in the
backyard mainly used to cook with wood close to the floor, in which domestic
animals roam freely), around the washboard (a place on the patio in which women
manually wash clothes), the water containers (open containers in which water is
collected when available) and the corral (a place on the patio in which the pigs
and cows spend the night). Animals walk around freely inside the houses. A
total of 123 dogs, 46 cats, 92 pigs, 32 cows and 15 rabbits were registered in
the 26 tested houses, all with free access into the premises.
2.2. Studydesign
The study was performed in two stages. During the ï¬rst stage, from August 2000 to July 2001, a head CT scan without
contrast was performed on 115 volunteers living in the
26 houses at the Puebla General
Hospital to diagnose NC.
Informed consent was obtained from all participants or their guardians. In
addition, three fecal samples were collected from 75 inhabitants and one blood
sample from 96 inhabitants. A coproparasitological study was done using direct
microscopical examination and the Faust and Graham method (Faust et al., 1938;
Graham, 1941). IgG antibody levels against T. solium cysticerci were determined
in the collected plasma samples by ELISA using T. solium cyst fluid following
the procedure reported by Chavarria et al. (2003). A sample was considered
positive if the optical density (OD) values were higher than 0.4 (mean of the
values obtained with Not-NC samples from the inhabitants of the same endemic
community plus 2 SD). During the second stage, soil samples were obtained in
the Autumn, Winter, Spring and Summer of 2001 to 2003
(Table 1). For additional analysis, a house was considered positive if Taenia
spp. eggs were found in at least one sample. The surface soil of each house was
swept, and samples of approximately 200 g soil were collected in plastic bags
at 2—10 cm depth from different parts of the house. Twenty gram soil samples
were kept under refrigeration and processed within a maximum period of72 h
after collection. Each sample was dried and passed through a 4 mm2 mesh to
remove debris. The remaining soil was cleaned by suspending it in puriï¬ed water and then centrifuging it at 300 g for 3 min. The
sediment was washed with 500 ml 1% Tween 80 solution in PBS and then shaken for
2 h and left to rest for 24 h until the supernatant was clear. Subsequently, twothirds of the
supernatant was removed. The sediments were suspended with the remaining
supernatant; samples were divided into two aliquots, placed into 15 ml tubes,
and centrifuged at 838 g for 10 min. Helminth eggs from soil samples were
recovered by a flotation method (Matsuo and Kamiya,
2005). Briefly, one tube of the sediment was suspended in 1.18-speciï¬c gravity zinc sulfate, stirred during 2 h in a high-speed vortex
and sieved through a 1 mm mesh. The suspension was centrifuged at 1000 g for 5 min. The process
was repeated twice. After this, samples were transferred to 15 ml tubes and
centrifuged again at 1000 g for 15 min. Tubes were ï¬lled to the top, and a coverslip (24 × 24 mm) was placed
on top of the tube. Coverslips were examined under a light microscope 2 h
later. The tube was covered with a new coverslip and left overnight to collect
the remaining eggs. For routine egg examination, the ether sedimentation
technique (Ritchie et al., 1960) was applied to the remaining sediment in the
aliquot tube. Briefly, the sediment was suspended in 10 ml 10% formalin,emulsiï¬ed and allowed to
ï¬x for at least 10 min. After that, 5 ml ether was added; tubes were then
stopped, inverted, vigorously shaken for 30 s and centrifuged at 425 g for 2 min. Four layers were
formed: solvent at the top, a debris plug, formalin, and sediment at the
bottom. The debris plug was loosened by ringing
376
M. Huerta et al.
Table 1 Frequency of parasites and parasite intensity found in the soil of
sampled households in the community of Tepetzitzintla, State of Puebla, Mexico
Spring (n = 109) Summer (n = 116) Autumn (n = 113) Winter (n = 53)
Frequency of Parasite Frequency of Parasite Frequency of Parasite Frequency of
Parasite parasitesa intensityb parasitesa intensityb parasitesa intensityb
parasitesa intensityb Hymenolepis nana Hymenolepis diminuta Giardia spp.
Ascaris spp. Taenia spp. Entamoeba spp. Enterobious vermicularis Sarcocystis
spp. Trichuris trichiura Entamoeba coli Balantinium coli
a b
3.7 0.9 2.7 52.2 43 34.8 8.2 1.8 10.1 7.3 31.1
0.04 0.009 0.05 1.28 0.43 0.92 0.13 0.10 0.12 0.23 0.53
0 0 0 19 7.8 0 0 0 10.3 0.9 1.7
0 0 0 0.31 0.08 0 0 0 0.13 0.01 0.03
21.2 3.5 14.1 41.5 29.2 31.8 19.5 10.6 19.5 37.2 17.6
0.36 0.07 0.32 0.88 0.30 0.49 0.42 0.20 0.31 0.88 0.37
9.4 7.5 11.3 24.5 17 20.7 15 9.4 26.4 28.3 26.4
0.11 0.09 0.23 0.41 0.17 0.30 0.32 0.15 0.45 0.60 0.74
Percentage of positive sampled areas = (number of positive areas/total number
of sampled areas) × 100.Parasite intensity = number of parasite eggs/number of
sampled areas.
with an applicator stick, and then the top three
layers were decanted. The sediment was mixed and removed with a disposable
pipette and one drop of sediment was covered with a 22 mm2 cover slip. A single
unstained wet mount was prepared from each concentrate. The entire coverslip
area was examined with an optical microscope at low power (×10); high power
(×40) was used in a similar fashion to identify and count eggs.
which includes the rainy months in Mexico. Ascaris
spp. and Taenia spp. were the main genera among the parasites detected.
3.2. Soil contamination with Taenia spp.
As Table 2 shows, the kitchen was the most infected place in terms of parasite
intensity and percentage of contaminated samples.
2.3. Statistical analysis
Data were processed in Excel 7.0 (Microsoft Corp., Redmond,
WA, USA)
and SPSS 10 (SPSS Inc., Chicago,
IL, USA).
Distribution of independent variables was compared by 2 tests with Yates’
correction, two-tailed Fisher’s exact tests or Student’s t test, using 95% CI.
3.3. Relation between NC and Taenia spp. soil contamination
CT scans were performed on 69 women and 46 men aged 5—79 years. Individuals
were classiï¬ed as silent-NC or nonNC according to
whether their CT scan images showed lesions compatible with NC, as previously described
(Fleury et al., 2003). In 14 individuals (ï¬ve men and
nine women), CT scans showedcalciï¬ed granuloma. Twelve individuals had a
single parasite, whereas two had multiple parasites. The 14 positive
individuals lived
in 12 households (in one house three NC cases were diagnosed), while the 101
NC-negative subjects lived in the remaining 14 houses. Table 3 shows that only
in the Summer was a signiï¬cant correlation between the presence of Taenia spp. eggs in soil
and NC
found (P = 0.05). Interestingly, as shown in Table 2, it was during the Summer when the lowest percentage of soil samples with
Taenia spp. eggs was detected (nine eggs in the 116 samples tested, 7.8%).
3. Results
3.1. Parasite contamination of soil
Two different parameters were deï¬ned to
measure parasite contamination: the percentage of positive sampled areas =
(number of positive areas/total number of sampled areas) × 100; and the
parasite intensity = number of parasite eggs/number of sampled areas. A total
of 391 soil samples was collected from the soil of
different areas of the sampled houses (Table 1). The total number of households
sampled was 26 in Autumn 2001, 14 in Winter 2001, 24 in Spring 2002 and 23 in
Summer 2003. Households in which eggs were detected were randomly distributed
in the community with no signiï¬cant geographical
aggregation (data not shown). Table 1 shows the different parasites found in
the soil of the sampled households throughout the four seasons, and their
frequency. The
lowest percentage of positive sampled areasand parasite intensity was found in
the Summer,
3.4. Relation between intestinal parasites and soil contamination
Coproparasitological studies were performed on the inhabitants of the 26 houses
included in this study. The following parasites were found: Ascaris
lumbricoides (9.3%), Entero-
Parasite contamination of soil in Mexican households
377
Table 2 Frequency of Taenia spp. eggs found in the soil of sampled households
in the community of Tepetzitzintla, State of Puebla, Mexico Outhouse Spring
Frequency of parasitesa Parasite intensityb Summer Frequency of parasitesa
Parasite intensityb Autumn Frequency of parasitesa Parasite intensityb Winter
Frequency of parasitesa Parasite intensityb Total frequency of parasitesa
a b
Backyard 48 (11/23) 1.74
Kitchen 55 (11/20) 2.05
Washboard 26.7(4/15) 0.47
Bucket 30.8 (4/13) 0.46
Corral 43.7 (7/16) 1.06
Total 43 (47/109)
45.4 (10/22) 1.64
10.5 (2/19) 0.16
10 (2/20) 0.10
5.3 (1/19) 0.16
5.3 (1/19) 0.053
10 (2/20) 0.15
5.3 (1/19) 0.053
7.8 (9/116)
28.6 (6/21) 0.81
14.3 (3/21) 0.29
41.2 (7/17) 0.94
47 (8/17) 1.35
31.6 (6/19) 0.47
22.2 (4/18) 0.33
30.1 (34/113)
12.5 (1/8) 0.375 27.1 (19/70)
7.7 (1/13) 0.154 22.1 (17/77)
25 (2/8) 0.75 32.8 (21/64)
18.2 (2/11) 0.182 24.2 (15/62)
14.3 (1/7) 0.29 22 (13/59)
33.3 (2/6) 0.33 23.7 (14/59)
16.9 (9/53)
Percentage of positive sampled areas = (number ofpositive areas/total number of
sampled areas) × 100. Parasite intensity = number of parasite eggs/number of
sampled areas.
bius vermicularis (7.3%), Hymenolepis nana (4.6%),
Trichuris trichiura (1.3%), Sarcocystis hominis (1.3%), Entamoeba coli (21.2%),
Entamoeba histolytica (11.9%), Giardia lamblia (6.6%), Lodamoeba buetschlii
(1.3%). No intestinal parasites were found in the inhabitants of only three of
the houses. In these three houses a smaller number of eggs was found in the
soil with respect to the number of parasites in the respective season (i.e. in
one house negative for coproparasites, only four parasites were detected in the
Spring, while 11 parasites were found in the overall soil inspection).
two different houses: one lived alone and revealed a
positive CT scan, while in the other house, all inhabitants showed negative CT
scans. Thus, coproparasitological studies did not correlate with NC diagnosis
(P = 0.70).
3.6. Anti-cysticercal antibodies do not correlate with CT scan diagnosis
Serum ELISA was performed on the plasma of 96 inhabitants of the community. As
previously reported (Fleury et al., 2003), no association was found between CT
scan and seropositivity (P = 0.18), although a signiï¬cant difference in optical densities (P = 0.008) was determined
between inhabitants with calciï¬ed NC (0.32 ± 0.24) and without NC (0.19 ± 0.11).
3.5. Taenia spp. eggs in coproparasitological studies do not correlatewith CT
scan diagnosis
Coproparasitological studies found Taenia spp. eggs in only two of the 75
inhabitants tested. These two subjects lived in
Table 3 Relation between computed tomography (CT) scan results and presence of
Taenia spp. eggs in the different seasons of the year in the community of
Tepetzitzintla, State of Puebla, Mexico Taenia spp. eggs in soil Spring + CT
scan households Positive Negative 11 9 − 1 3 P 0.59 Summer + 5 1 −
5 12 P 0.05 Autumn + 11 10 − 1 4 P 0.33 Winter + 3 3 − 4 4 P 1
378
M. Huerta et al. Moreover, it is also possible that Taenia spp. eggs can
survive in the environment for weeks, as has been reported for other taeniids
(Gemmell and Johnstone, 1976), spreading the disease by overdispersion. Many
epidemiological studies performed in rural areas of Mexico (Diaz Camacho et
al., 1991; Sarti-Guti´rrez et al., 1988) and other endemic e countries (Ferrer
et al., 2003; Garc´ et al., 2003) have A±a determined risk factors related to
human cysticercosis seroprevalence, i.e. history of seizures, human behavior
(particularly poor hygiene), pig-rearing practices, household use of toilets
and the presence of a tapeworm carrier in the house (Sarti et al., 1992).
However, the identiï¬cation of risk factors related
to human NC infection has remained elusive. In two epidemiological studies
based on CT scans performed in Mexican rural communities, none of the above
risk factors was found to be associated withNC (Fleury et al., 2003, 2006). In the present
study, we found, for the ï¬rst time, a high
level of Taenia spp. egg contamination in the different household areas tested,
pointing to the relevance of appropriate standardized techniques such as PCR to
speciï¬cally diagnose the source of the detected Taenia spp. eggs. Such techniques
will allow the detection of endemic areas with high transmission of the
respective cestodiasis. Nevertheless, the ï¬nding of such
a high level of contamination with Taenia spp. eggs is a clear indicator of the need to
improve hygienic conditions in rural areas. The detection of Taenia spp. eggs
in soil and water has been reported previously only by Diaz Camacho et al.
(1991). However, these authors found only one soil sample with Taenia spp.
eggs. The procedure used for egg detection in soil, as well as the different
living standards and the lower T. solium prevalence between Northern and Central Mexico, could underlie the differences between
that study and the present study. Herein, a signiï¬cant correlation between CT scan results and detection of eggs in
soil was found in the Summer season. The absence of
correlation in the other seasons, in this part of Mexico, could be the consequence of
the larger number of eggs and their more effective dispersion during the drier
seasons. Interestingly, detection of Taenia spp. eggs in the households was
found to be a more predictive parameter to identify NCinhabitants than the
detection of Taenia spp. eggs in feces, as coproparasitological studies have
not proved to be a predictive parameter of NC cases. This could be due to the
short period that tapeworm infections last, as was reported by Garc´ et al.
(2003). In addition, the levA±a els of anti-cysticercal antibodies were also
found to be a predictive parameter to identify NC cases. The present results
may indicate a high risk of infection with Taenia spp. within the household,
with important potential impact on human health, which should be further
analyzed. The high level of parasite contamination of the soil may also serve
to alert authorities and the population of the need to control the environment
to prevent human infections.
3.7. Taenia spp. eggs in coproparasitological studies and plasma Ab levels do
not correlate with Taenia spp. eggs in soil
A house was considered serologically positive when it
was occupied by at least one inhabitant with positive plasma Ab levels (OD >
0.4). No signiï¬cant relation was found between Ab levels
and the presence of Taenia spp. eggs in soil (P = 0.91 in Spring,
P = 0.95 in Summer,
P = 0.25 in Autumn and P = 0.21 in Winter). An additional analysis was
performed considering a house as positive according to the coproparasitological
examination if Taenia spp. eggs were detected in at least one of its
inhabitants. No signiï¬cant relation was found
between coproparasitological results and thepresence of Taenia spp. eggs in
soil.
4. Discussion
This study clearly documents the signiï¬cant soil
contamination in rural areas by parasites that can potentially affect human
health. Results
are in accordance with the high frequency of intestinal parasites found in the
inhabitants of this community. Indeed, in only three out of the 26 houses,
coproparasitological studies detected no intestinal parasites. Several factors
can contribute to the high level of parasite contamination in the soil: many
domestic animals walking freely in the house, in particular dogs, cats and
pigs; the lack of compartmentalization of the houses and the presence of soil
floors; and the fact that most of the inhabitants have intestinal parasites.
Considering the hyperendemicity of T. solium in the rural community in which
this study was performed, the ï¬nding of Taenia spp.
eggs in the soil was emphasized. There are higher proportions of
Taenia-positive soil samples and parasite intensity in Spring,
which could indicate that the environmental conditions are favorable for egg
development during this season. Several factors, such as climatic and
environmental conditions, the texture of the analyzed soil and the presence of
domestic animals, may have contributed to this ï¬nding. The
seasonal dynamics of parasitic infections has been reported previously for
different parasites (Theodoropoulos et al., 2000; Vlassoff et al., 2001).
Although the most positivesamples were found in the kitchen, it is worth noting the high
Taenia spp. egg prevalence in all the tested household areas. The high presence
of Taenia spp. eggs in the superï¬cial layer of soil
supports the notion that this contamination focus is a crucial instrument in its dissemination.
Of particular interest is the high frequency of households with Taenia spp.
eggs in the soil (99 of the 391 soil samples, 25.3%) compared with the
apparently rare tapeworm carriers (two of the 75 fecal samples, 2.7%) according
to coproparasitological studies. It is possible that the detected Taenia spp.
eggs were from other cestodes that can infect domestic animals. The appearance
of eggs in the soil does not allow distinction between taeniids, in particular
between T. solium, T. saginata, T. pisiformis and Echinococcus spp. It is
highly possible that most of the eggs found in soil were from the many dogs and
cats that have free access to all areas of the houses.
Authors’ contributions: MHu, TG, GF, AF and ES designed the study protocol; AF
carried out the clinical assessment; MHe carried out the immunoassay
determination; JJM, GF, AF and ES carried out the analysis and interpretation
of the data; RA and HHJ carried out the coproparasitoscopic studies; MHu, RD,
JD and MEDH carried out the ï¬eld work; EG
Parasite contamination of soil in Mexican households and TA provided laboratory
support; GF, AF and ES drafted the manuscript. All authorsread and approved the
ï¬nal manuscript. AF and ES are guarantors of
the manuscript. Acknowledgements: The authors are grateful to the authorities of
the Secretar´ de Salud del Estado de Puebla, A±a Puebla,
Mexico, for the support to this project. We are also A±a grateful to Mercedes
Baca for technical assistance and Mar´ Isabel P´rez Montfort for the correction
of the English vere sion of the manuscript. Funding:
Consejo Nacional de Ciencia y Tecnologia (200401-040, 46953-M), Mexico, the Facultad de Medicina, Benemerita Universidad de Puebla, Puebla,
Mexico, and the Howard
Hughes Medical Institute, United
States. Conflicts of interest: None
declared. Ethical approval: The Ethical Committee of the National Institute for
Neurology and Neurosurgery (Instituto Nacional de Neurolog´ y Neurocirug´
Mexico City, Mexico A±a A±a),
379
Fleury, A., Gomez, T., Alvarez, I., Meza, D., Huerta, M., Chavarria, A.,
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C., Sciutto, E., Fragoso, G., 2003. High prevalence of
calciï¬ed silent
neurocysticercosis in a rural village
of Mexico. Neuroepidemiology
22, 139—145. Fleury, A., Morales, J., Bobes, R.J., Dumas, M.,
Y´nez, O., Pi˜a, J., a n Carrillo-Mezo, R., Mart´
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