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UDC: 616.994.253-036.22-055.2:614.253.8(575.1)
COMPARATIVE ANALYSIS OF MEDICAL LITERACY LEVELS AND CERVICAL
CANCER RISK FACTORS AMONG WOMEN IN THE REPUBLIC OF
KARAKALPAKSTAN
Bazarova Seregul Kalmurzaevna
Department of obstetrics, gynecology and neonatology
Karakalpakstan Medical Institute
ABSTRACT:
Objective: To conduct a comparative analysis of the level of medical literacy
regarding cervical cancer (CC) and to identify the prevalence of its main risk factors among
women living in different districts of the Republic of Karakalpakstan. Methods: A cross-
sectional anonymous survey was conducted among 1,500 women aged 25-49. A specially
designed questionnaire was used to assess awareness of CC, human papillomavirus (HPV),
screening methods (Pap test, HPV test), HPV vaccination, and key risk factors (smoking, early
sexual debut, number of partners). Statistical analysis was performed to compare data between
urban (Nukus city) and rural populations. Results: The study revealed a generally low level of
medical literacy on CC issues. Only 35% of respondents were aware of the link between HPV
and CC. Women in rural areas demonstrated significantly lower awareness compared to urban
residents (p < 0.001). A high prevalence of risk factors was identified: 28% of respondents were
smokers, and 45% reported an early sexual debut (before age 18). A significant negative
correlation was found between the level of medical literacy and the presence of behavioral risk
factors. Conclusion: There is a critical need to increase medical literacy about cervical cancer
and its prevention among women in Karakalpaikstan, with a particular focus on rural areas. The
findings justify the need for targeted educational programs and the development of accessible
screening services to reduce the incidence and mortality of cervical cancer in the region.
Keywords:
cervical cancer, HPV, medical literacy, health awareness, risk factors, screening, Pap
test, Karakalpakstan, women's health.
СРАВНИТЕЛЬНЫЙ АНАЛИЗ УРОВНЯ МЕДИЦИНСКОЙ ГРАМОТНОСТИ И
ФАКТОРОВ РИСКА РАКА ШЕЙКИ МАТКИ СРЕДИ ЖЕНЩИН РЕСПУБЛИКИ
КАРАКАЛПАКСТАН
Базарова Серегул Калмурзаевна
Кафедра акушерства, гинекологии и неонатологии
Медицинский институт Каракалпакстана
АННОТАЦИЯ
Цель: Провести сравнительный анализ уровня медицинской грамотности в отношении
рака шейки матки (РШМ) и выявить распространенность его основных факторов риска
среди женщин, проживающих в различных районах Республики Каракалпакстан. Методы:
Проведено одномоментное анонимное анкетирование 1500 женщин в возрасте 25-49 лет.
Для оценки осведомленности о РШМ, вирусе папилломы человека (ВПЧ), методах
скрининга (Пап-тест, ВПЧ-тест), вакцинации против ВПЧ и ключевых факторах риска
(курение, раннее начало половой жизни, количество партнеров) использовалась
специально разработанная анкета. Статистический анализ проводился для сравнения
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данных между городским (г. Нукус) и сельским населением. Результаты: Исследование
выявило в целом низкий уровень медицинской грамотности по вопросам РШМ. Лишь 35%
респондентов знали о связи ВПЧ и РШМ. Женщины в сельской местности
продемонстрировали значительно более низкую осведомленность по сравнению с
городскими жительницами (p < 0,001). Выявлена высокая распространенность факторов
риска: 28% опрошенных являлись курильщицами, 45% указали на раннее начало половой
жизни (до 18 лет). Обнаружена достоверная отрицательная корреляция между уровнем
медицинской грамотности и наличием поведенческих факторов риска. Заключение:
Существует острая необходимость в повышении медицинской грамотности по вопросам
рака шейки матки и его профилактики среди женщин Каракалпакстана, с особым
акцентом на сельские районы. Полученные данные обосновывают необходимость
внедрения целевых образовательных программ и развития доступных скрининговых
служб для снижения заболеваемости и смертности от РШМ в регионе.
Ключевые слова:
рак шейки матки, ВПЧ, медицинская грамотность, осведомленность о
здоровье, факторы риска, скрининг, Пап-тест, Каракалпакстан, женское здоровье.
INTRODUCTION
The health and development of children are intricately linked to the quality of their environment.
Environmental factors, including air and water quality, nutrition, and exposure to toxic
substances, can have profound and lasting effects on physiological processes, especially during
critical periods of growth (World Health Organization, 2018). The Aral Sea crisis represents one
of the most severe anthropogenic ecological disasters of the 20th century. The desiccation of the
sea has given rise to the Aralkum, a vast salt desert, which has become a source of intense dust
and salt storms that transport a toxic mix of salt, pesticides, herbicides, and heavy metals over
thousands of kilometers (Micklin, 2016).
The population of the Aral Sea region, particularly in Karakalpakstan, has been exposed to this
complex of adverse factors for several generations. This chronic exposure has been linked to a
wide range of health problems, including high rates of respiratory diseases, anemia, kidney and
liver pathologies, and various forms of cancer (Crighton et al., 2011). While the systemic health
impacts are well-documented, the specific effects on the development of the oral and
maxillofacial system in children remain a less explored area.
The development of the dentoalveolar system is a multifactorial process influenced by both
genetic and environmental determinants. Proper formation of teeth, growth of maxillary and
mandibular bones, and the establishment of a stable occlusion depend on adequate nutrition,
proper functional stimuli (such as nasal breathing and mastication), and the absence of systemic
toxic exposures (Proffit et al., 2018). Environmental stressors prevalent in the Aral Sea region
can potentially disrupt this delicate developmental process through several mechanisms. Firstly,
contaminated drinking water with high salinity and levels of heavy metals (e.g., lead, cadmium)
can interfere with enamel and dentin mineralization, leading to structural defects and increased
susceptibility to caries. Secondly, nutritional deficiencies, particularly of calcium, phosphorus,
vitamin D, and proteins, resulting from degraded agricultural land and poor socioeconomic
conditions, can impair skeletal growth, including that of the jaws (Moyers, 1988). Thirdly, the
high prevalence of respiratory illnesses caused by chronic inhalation of dust can lead to habitual
mouth breathing. This altered breathing pattern disrupts the natural balance of orofacial
musculature, often resulting in characteristic dentoalveolar anomalies such as maxillary
constriction, posterior crossbite, and anterior open bite (Linder-Aronson, 1979).
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Given the unique and severe environmental challenges in the Aral Sea region, it is hypothesized
that children living there exhibit a higher prevalence and a distinct pattern of dentoalveolar
anomalies (DAA) compared to children from ecologically favorable regions. This study aims to
test this hypothesis by conducting a comparative analysis of the prevalence and structure of
DAA in pediatric populations from the Aral Sea region and a control area. The findings are
expected to provide crucial insights for developing targeted preventive and therapeutic public
health strategies for this vulnerable population.
MATERIALS AND METHODS
Study design and population -
A comparative, cross-sectional epidemiological study was
conducted between September 2023 and May 2024. The study population consisted of children
aged 7 to 14 years, a period encompassing the mixed and early permanent dentition stages,
which are critical for the development of occlusion.
The main group (MG) comprised 450 children (220 boys, 230 girls) who were permanent
residents of the Muynak and Kungrad districts of the Republic of Karakalpakstan. These districts
are located in the immediate vicinity of the desiccated Aral Sea and are most affected by the
ecological crisis. The inclusion criteria for the MG were: continuous residence in the specified
area since birth and the absence of severe congenital syndromes affecting craniofacial growth.
The control group (CG) consisted of 450 children (225 boys, 225 girls) of the same age range
from the Parkent district of the Tashkent region. This area was selected due to its relatively
favorable ecological conditions, distance from major industrial polluters, and similar
socioeconomic and ethnic composition to the main group, minimizing potential confounding
variables.
Ethical approval for the study was obtained from the Ethics Committee of the Tashkent State
Dental Institute. Written informed consent was obtained from the parents or legal guardians of
all participating children prior to their inclusion in the study.
Data collection -
Data were collected through two primary methods: a clinical dental
examination and a structured questionnaire.
Clinical Examination: All examinations were performed by a team of two calibrated
orthodontists in a dental clinic setting under standardized conditions using artificial light, a
dental mirror, and a periodontal probe. The assessed parameters included the occlusal
relationship, where the molar relationship was classified according to Angle's classification
(Class I, Class II, Class III). In the sagittal plane, overjet was measured in millimeters from the
labial surface of the most prominent maxillary incisor to the labial surface of the corresponding
mandibular incisor. For the vertical plane, overbite was measured as the vertical overlap of the
maxillary incisors over the mandibular incisors, expressed in millimeters or as a percentage, and
an open bite was recorded if no vertical overlap was present. In the transversal plane, the
presence of a posterior crossbite (unilateral or bilateral) was recorded. Dental arch anomalies
such as dental crowding or spacing were assessed using the Little's Irregularity Index for the
lower incisors and visual assessment for other areas. Additionally, the presence of individual
tooth anomalies in position, shape, or number, and the condition of the enamel, specifically for
enamel hypoplasia or other developmental defects, were recorded. Inter-examiner reliability was
assessed by re-examining 10% of the sample, with a Kappa coefficient of 0.89 indicating a high
level of agreement.
Questionnaire: A structured questionnaire was administered to the parents or guardians of the
children to gather information on demographics such as age, sex, and place of residence. It also
collected data on environmental exposure, including the duration of residence in the region, the
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primary source of drinking water (tap, well, bottled), and the perceived frequency of dust storms.
The medical history section covered chronic respiratory diseases (rhinitis, asthma), allergies, and
habits like mouth breathing or thumb sucking. Finally, dietary habits were assessed by recording
the frequency of consumption of key food groups, including dairy products, fresh fruits and
vegetables, and meat/fish.
Statistical analysis -
The collected data were entered into a database and analyzed using IBM
SPSS Statistics for Windows, Version 26.0. Descriptive statistics (frequencies, percentages,
means, and standard deviations) were calculated to summarize the data. The Chi-square (χ²) test
was used to compare the prevalence of different types of DAA and categorical variables between
the main and control groups. The independent samples t-test was used for comparing continuous
variables. A p-value of less than 0.05 was considered statistically significant. Logistic regression
analysis was performed to identify the key risk factors associated with the presence of DAA.
RESULTS
Demographic characteristics -
The study included a total of 900 children. The main group
consisted of 450 children with a mean age of 10.5 ± 2.1 years, and the control group consisted of
450 children with a mean age of 10.3 ± 2.3 years. There were no statistically significant
differences in age (p=0.18) or gender distribution (p=0.75) between the two groups, confirming
their comparability.
Prevalence of dentoalveolar anomalies -
A striking difference was observed in the overall
prevalence of DAA between the groups. In the main group (Aral Sea region), 397 out of 450
children (88.2%) were diagnosed with at least one form of DAA. In contrast, in the control group,
DAA was identified in 209 out of 450 children (46.5%). This difference was highly statistically
significant (χ² = 186.4, p < 0.001).
Structure of dentoalveolar anomalies - The distribution of specific types of DAA also varied
significantly between the two groups, as detailed in Table 1.
Table 1: Prevalence of Specific Dentoalveolar Anomalies in the Main and Control Groups
Anomaly type
Main group (n=450) Control group (n=450) p-value
Sagittal Anomalies
Angle class II malocclusion 142 (31.6%)
75 (16.7%)
<0.001
Angle class III malocclusion 55 (12.2%)
18 (4.0%)
<0.001
Increased overjet (>3mm)
168 (37.3%)
81 (18.0%)
<0.001
Vertical anomalies
Deep bite (>3mm)
151 (33.6%)
92 (20.4%)
<0.001
Anterior open bite
61 (13.6%)
15 (3.3%)
<0.001
Transversal anomalies
Posterior crossbite
78 (17.3%)
25 (5.6%)
<0.001
Dental arch anomalies
Crowding
210 (46.7%)
105 (23.3%)
<0.001
Spacing
45 (10.0%)
31 (6.9%)
0.110
Enamel defects
Enamel hypoplasia
95 (21.1%)
22 (4.9%)
<0.001
Children in the Aral Sea region demonstrated a significantly higher prevalence of nearly all types
of malocclusion. Sagittal anomalies, particularly Angle Class II and increased overjet, were
approximately twice as common in the main group. The prevalence of anterior open bite and
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posterior crossbite, anomalies often associated with altered respiratory function, was over four
and three times higher, respectively, in the main group compared to the control group.
Furthermore, dental crowding and developmental enamel defects were significantly more
frequent among children from the ecologically disadvantaged region.
Association with environmental and health factors -
The analysis of the questionnaire data
revealed significant associations between the presence of DAA and several risk factors within
the main group (Table 2).
Table 2: Risk Factor analysis for DAA within the main group (n=450)
Factor
DAA
present
(n=397)
DAA
absent
(n=53)
Odds
ratio
(95% CI)
p-
value
Primary drinking water source
- Tap/well water
355 (89.4%)
38 (71.7%)
3.8 (1.9 - 7.6)
<0.001
- Bottled/filtered water
42 (10.6%)
15 (28.3%)
Ref.
History
of
chronic
Respiratory disease
188 (47.4%)
11 (20.8%)
3.4 (1.7 - 6.8)
<0.001
Reported Mouth Breathing
Habit
155 (39.0%)
8 (15.1%)
3.6 (1.6 - 8.1)
0.001
Low Dairy Consumption
(<3/week)
291 (73.3%)
25 (47.2%)
3.1 (1.7 - 5.5)
<0.001
Children in the main group who primarily consumed local tap or well water had a 3.8 times
higher odds of having DAA compared to those who consumed bottled water. A reported history
of chronic respiratory disease and habitual mouth breathing were also strong predictors,
increasing the odds of DAA by 3.4 and 3.6 times, respectively. Furthermore, a diet low in dairy
products, serving as a proxy for calcium intake, was significantly associated with a higher
likelihood of DAA.
DISCUSSION
The findings of this study provide compelling evidence that the severe and multifaceted
environmental degradation in the Aral Sea region is a major contributor to the poor dentoalveolar
health of the pediatric population. The prevalence of DAA in children from this region was
found to be 88.2%, nearly double the rate observed in the control group (46.5%), a figure that is
alarming from a public health perspective. This confirms the primary hypothesis of the study and
aligns with broader research demonstrating the impact of environmental stressors on child
development (Landrigan et al., 2017).
The structure of the anomalies observed offers insight into the potential causal pathways. The
significantly higher rates of anterior open bite (13.6% vs 3.3%) and posterior crossbite (17.3% vs
5.6%) in the main group strongly support the "respiratory distress" hypothesis. Chronic
inhalation of dust and salt from the Aralkum is a known cause of respiratory and allergic
diseases in the region (Crighton et al., 2011). These conditions often force children into a pattern
of habitual mouth breathing. According to the functional matrix theory, this altered breathing
pattern disrupts the equilibrium of the orofacial muscles, leading to a low tongue posture,
insufficient lateral stimulation of the maxilla by the tongue, and over-activity of the buccinator
muscles. This cascade results in a narrow, high-arched palate, posterior crossbite, and an open
bite tendency (Proffit et al., 2018; Linder-Aronson, 1979). Our data, showing a strong
association between DAA and reported respiratory illness and mouth breathing, corroborates this
mechanism.
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The high prevalence of enamel hypoplasia (21.1% vs 4.9%) points towards systemic
disturbances during tooth development. This could be a result of two primary factors. First, the
chronic ingestion of contaminants through water and food. The Aral Sea basin is heavily polluted
with pesticides (like DDT), defoliants, and heavy metals from decades of intensive cotton
production (Micklin, 2016). These toxins can interfere with the function of ameloblasts, the cells
responsible for enamel formation, leading to developmental defects. Second, widespread
nutritional deficiencies play a critical role. Our questionnaire data indicated significantly lower
consumption of dairy products and likely other micronutrient-rich foods in the main group.
Deficiencies in calcium, vitamin D, and vitamin A are known to cause enamel hypoplasia and
impair the overall mineralization of skeletal and dental tissues (Moyers, 1988).
Furthermore, the overall increase in malocclusion severity, including crowding and sagittal
discrepancies, likely reflects the combined effect of these factors. Poor nutrition can lead to a
failure of the jaws to reach their full genetic growth potential, resulting in a discrepancy between
jaw size and tooth size, which manifests as crowding. Systemic toxicity and chronic illness can
further disrupt the complex hormonal and cellular signaling that governs coordinated craniofacial
growth.
The study has several limitations. Its cross-sectional design establishes association but cannot
definitively prove causation. The questionnaire data relies on parental recall, which may be
subject to bias. While we selected a control group with similar demographic profiles,
unmeasured confounding variables may still exist. Future research should include longitudinal
studies to track developmental trajectories and direct biochemical analysis of environmental
samples (water, soil) and biomarkers in children (e.g., heavy metal levels in hair or blood) to
establish more direct causal links.
Despite these limitations, the implications of our findings are significant. They highlight an
overlooked public health crisis within the broader Aral Sea disaster. The high burden of DAA
not only affects aesthetics and psychosocial well-being but also impairs masticatory function,
phonetics, and can increase the risk of periodontal disease and temporomandibular disorders in
the long term.
CONCLUSION
This study demonstrates a significantly higher prevalence and a specific, more severe pattern of
dentoalveolar anomalies in children living in the ecologically distressed Aral Sea region
compared to a control population. The evidence suggests that this is a consequence of a complex
interplay of environmental factors, including exposure to contaminated water and dust, chronic
respiratory illnesses leading to altered orofacial function, and widespread nutritional deficiencies.
The dentoalveolar system serves as a sensitive indicator of a child's overall health and
environmental exposure. The findings call for urgent and integrated public health interventions.
These should include: (1) implementation of programs to provide access to safe drinking water;
(2) large-scale dental screening programs for early detection and interception of developing
malocclusions; (3) nutritional support initiatives, including supplementation with essential
vitamins and minerals; and (4) collaboration between dental professionals, pediatricians, and
environmental health specialists to address the root causes of these health disparities. Addressing
the oral health of children in the Aral Sea region is an essential and integral part of mitigating the
devastating human consequences of this ecological catastrophe.
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