Monday, 31 May 2021

Iris publishers-Global Journal of Nutrition & Food Science (GJNFS)

 

Prevalence of Malnutrition and Stunting in Under Five Creche of a Rural Private School in Owerri North, Imo State

Authored by EN Onyeneke*

Abstract

The prevalence of malnutrition and stunting in under five Creche of any rural private school in Owerri North L. G. A was investigated. Owerri North is made up of seven districts namely Egbu, Emekuku, Emii, Ihitte/Ogada/Oha, Naze, Obibi-Uratta and Orji. A random selection of four schools were made and the schools include; Oxford Foundation Academy, Ulakwo, Rhema Kiddies School, Amaorie, Noble Star Academy, Orji and St. Carols Nursery and Primary School, Ulakwo. These schools were selected because they meet the set out standard and quality for Nursery Education. The study adopted a cross-sectional design involving 250 pupils from four schools. Simple random selection by balloting was used to select the children from the schools. The questionnaire was validated and pre-tested by lecturers in the Nutrition and Dietetics Department, and data on anthropometric indices- weight and height, BMI and MUAC; socio-demographic status, dietary pattern and frequency of food consumption were collected. Results obtained showed that one hundred and twelve (44.8%) under five were males while 138 were females (55.2%). About 209 (83.6%) were from Imo state and of the Igbo ethnic group240 (96%). Five (2%) of the respondents were between the ages of 6 to 12 months, 114 (45.6%) were aged between 1 to 3 years, and 130 (52%) were aged 3 to 5 years. The socio-demographic data of the respondents showed that the 70 (28%) of the respondents’ fathers were civil servant, 94 (37.6%) were traders and 27 (10.8%) were farmers. Fifty (20%) of the respondents’ mothers were civil servants, 134 (53.6%) were traders and 25 (10%) were farmers, while 41 (16.4%) were of other occupations. Monthly income distribution of the children’s parents showed that 29 (11.6%) earned ₦10,000-50,000, 119 (47.6%) earned ₦50,000 – 100,000, 96 (38.4%) earned above ₦100,000. Data from living condition showed that 154 (61.6%) live in a bedroom flat, 44 (17.6%) live in one room apartment and 39 (15.6%) live in public yard. Data on the dietary practices of the children’s care givers showed 221 (88.4%) prepared food at home to feed the children, (78.4%) eat three times in a day, 214 (85.6%) took in-between meals and 173 (69.2%) took snacks as in-between meals. About 243 (97.2%) consumed fruits and vegetables, of which (55.2%) were frequent, 66 (26.4%) twice in a week and 36 (14.4%) occasionally. Data from the frequency of food consumption from various food groups showed that 97 (38.8%) of the children consumed cereals and their products on a daily basis, 92 (36.8%) consumed cereals 3 to 4 times in a week. Starchy roots and tubers consumption showed that 98 (39.2%) consumed roots and tubers three to four times weekly, 88 (35.2%) once to twice weekly. One hundred and seven (42.8%) consumed legumes and its products once to twice weekly, 83 (33.2%) three to four times weekly, while 119 (47.6%) consumed vegetables daily, and 82 (32.8%) consumed fruits once to twice per week with additional 79 (31.6%) daily. Data on milk and milk products consumption showed that 92 (36.8%) consumed milk three to four times weekly and 62 (24.8%) daily. The prevalence of wasting among the under-five was 2.8%, stunting 3.2%, and underweight was 1.6%. The mid-upper arm circumference measurement showed that only 3 (1.2%) of the children were malnourished, while 242 (96.8%) were normal. This study shows that stunting, underweight and wasting results from a complex interaction of factors. Poor Socioeconomic and environmental conditions are important determinants of nutritional status. Poor nutrition knowledge as a re3sult of limited access to nutrition education also leads to poor food choice by the mothers. Therefore, education of women should be treated with utmost priority because it will help raise the standard of living of the family and pave way for a better socio-economic status and healthier food choice.

Keyword: Anthropometric indices; Feeding habit; Health; Nutritional status; Private schools; Nigeria

Introduction

The concept of malnutrition and stunting in under five kids is not foreign to the ear. Theoretically, malnutrition is a term that refers to both under nutrition and over nutrition. People are malnourished if the calories and protein they take through their diet are not sufficient for their growth and maintenance due to ill health, they are not able to make complete use of the food they eat (under nutrition) or if they consume too many calories (over nutrition). In this paper, we consider under nutrition and malnutrition equivalently [1]. The physical and /or mental development of children can be hampered by poor nutrition during childhood which consequently may lead to a greater risk of casualty from communicable diseases or additional critical infection which ultimately end in a bigger economic burden of a society. Evidently, malnutrition among children and mothers adversely affect the growth of development in both national and international economic arena as well as health and sustainable developments. Malnutrition is the salient source of 3.5 million deaths globally and responsible for 35% of the morbidities among children under five which undoubtedly, defines malnutrition as a prime cause for critical health and development disorders faced by people, mostly children in developing countries Characteristics of children suffering from malnutrition include stunting or chronic malnutrition (low height for age), wasting or acute malnutrition (low weight fit height ) or being underweight for their age (United Nations 4th report ,2000). Stunting is the impaired growth and development that children experience from poor nutrition, repeated infection, and inadequate psychosocial stimulation. Children are defined as stunted if their height -for-age is more than two standard deviations below the WHO Child Growth Standards median (WHO, 2019).

Many of us use the words Daycare, Crèche, Educare, Nursery school and Pre-primary fairly interchangeably. However, some mother’s become quite upset when they realise the type of care their toddler or pre- schooler is receiving is not what they had been expecting. A crèche or day care facility offers supervised play for babies and young toddlers. The staff may have certificates in childcare but won’t necessarily have degrees in early childhood development. There are toys and lots of fun and the needs of your child is being taken care of with meal, snacks, naps, changing times and some even do potty training at a set stage (though there is much debate around this ,as many believe that potty training when children are ready is more successful) [2].

Globally, prevalence of stunning amongst school age children typically varies from place to place ranging from 9.3-24.0% in Latin America and Carribean to as high as 20.2-48.1 in Africa. In South Africa the prevalence for stunting is 18.0% whereas it is as high as 42.0% and 50.0% in mid and Eastern Africa respectively. Nationally, prevalence of stunting among primary school children ranges from 11.5% in Anambra, 11.8% in Onitsha to as high as 60% in Kebbi State. In Nigeria, the progress towards halving the proportion of people suffering from hunger under the Millennium Development Goals (MDGs) has hitherto been slow and daunting. Stunting has profound effects on the health of children. It predisposes to heightened risks of severe infection as a result of immune compromised responses. Stunting has also been implicated in increased morbidity and mortality, reduced physical, neurodevelopmental and economic capacity and an elevated risk of metabolic diseases diseases adulthood. Under nutrition significantly interferes with a number of bodily functioned such as immunity (cell -mediated immune responses) antibody responses and cytokine production that as a result provoke poor health outcomes in early infancy and childhood. Most importantly, the high prevalence of bacterial and parasitic diseases in poor and developing countries have continued of exacerbate the effect of stunting in children.

Risks of stunting are high in children as a result of heightened vulnerabilities to low dietary intake, inaccessibility to food, inequitable distribution of food within the household, improper food storage and preparation, dietary taboos and infectious diseases. Significant associations have been established between early childhood stunting and late onset adulthood depression with elevated self - reported conduct problems. The consequences of stunting iterated above demonstrate the need to investigate and implement interventions to address the problem amongst school children. Furthermore, the ‘double burden of malnutrition’, (in which households have a stunted child and an overweight mother) makes stunting as a form of under nutrition quite worrisome. Numerous studies have investigated and provided broader national estimates of stunting, even though key health-related targets in the Millennium Development Goals and the Sustainable Development Goals supports concerted calls to eradicate poverty and hunger whilst also bridging inequities in health. Bearing this in mind, there is a dire need for comparative statistics across wealth quintiles and vulnerable populations that can inform formulation and adoption of feasible policies at the strategic and operational levels of government in order to curtail the effects of stunting in Nigeria. The prevalence of malnutrition and stunting occurs mainly in children especially the under five. In Nigeria, the economic situation of the country has led to malnutrition and stunting. Hence, the knowledge of the effects of malnutrition will aid in the consumption of adequate diet to increase the healthiness of the population. It was therefore important to study how malnutrition affects the health of an individual and may lead to chronic health effect. The general objective of the study is to examine the prevalence of malnutrition and stunting in Under five (5) creche in rural private Nursery Schools in Owerri North L.G.A.

The benefits that could be deprived from the outcome of the research work are as follows:

1. Identification of the causes of poor nutrition on children and the implementation of the recommendation suggestions by various nutritional bodied which will lead to better and healthy generation,

2. Provides useful information on the alarming rate of malnutrition in the country and how it will be reduced and

3. The result of the work can be used as models by government and all health workers on child right and wellbeing.

Materials and methods

Study area

Owerri is located within the Southeast Part of Nigeria and lies at Latitude 50 27-50 31’N and longitude 6055-7003’E, it is the capital of Imo State. Owerri North is made up of seven districts namely Egbu, Emekuku, Emii, Ihitte/Ogada/Oha, Naze, Obibi-Uratta and Orji. The 12 wards in Owerri North L.G.A are Agbala/Obube/ Ulakwo, Awaka/Ihitte Ogada, Egbu, Emekuku i, Emekuku ii, Emii, Ihitte Oha, Naze, Obiibi Uratta I, Obiibi Uratta ii, Obibiezena, Orji. A random selection of four schools were made and the schools include; Oxford Foundation Academy, Ulakwo, Rhema Kiddies School, Amaorie, Noble Star Academy, Orji and St. Carols Nursery and Primary School, Ulakwo. These schools were selected because they meet the set out standard and quality for Nursery Education.

Survey design

A cross sectional study of 250 pupils from four schools.

Sample selection

Simple random selection by balloting was used to select the children from the schools.

Sample size determination

The formula of YaroYahmen (1974) as presented in equation (1) was used for the samples size determination.

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Where n = sample size; N = population size = 100; 1 = constant; e= margin of error (5% or 0.05) and by solving the equation (1), N = 518 and from calculation, n = 250

Data collection

The instruments used include;

Questionnaire: The questionnaire was validated and pre-tested by lecturers in the Nutrition and Dietetics Department, it was done for reliability and validity of the study. The questionnaire was made to pass round and get to every child, taken home to be filled by their parents or caregiver then returned the next day. I took their anthropometric measurement before the questionnaires were taken home.

Anthropometry: Anthropometric measurement and BMI of each child was calculated.

Height measurement: The height was measured barefooted to the nearest 0.01m, a standard deliberate stadiometer was used with the subject (child), standing erect and the feet parallel and held buttocks, shoulders and back of the child upright. Then with the head held comfortably erect with both hands hanging by the side.

Body Mass Index (BMI): BMI is a number that associates a person’s weight with his or her height/length. The formula used to calculate BMI is as follows: weight in kg divided by length in metres squared (Weight in kg ÷ height in metres m²). A BMI over 18.5 indicates adequate nutrition; below 16 is an indication of energy deficiency, BMI between 25 and 30 indicates over nutrition, whereas >30 BMI indicate obesity. The weight categories for children are defined as follows; Under weight is BMI of less than the 5th percentile ; Normal weight is a BMI from the 5th percentile to below the 85th percentile; Overweight is a BMI above the 85th percentile to below the 95th percentile and Obese is a BMI greater than or equal to the 95th percentile.

Mid Upper Arm Circumference (MUAC): The MUAC gives an indication of the degree of wasting and stunting and is a good predicator of mortality. Research shows that it is equally good, than other measurement for screening young children. The MUAC was measured using a MUAC tape. MUAC is the circumference of the left upper arm and is measured at the midpoint between the tip of the shoulder and elbow.

Data analysis

The data was collected according to the children’s age. Weight and height parameters was used to obtain their BMI; Statistical package for social science version 20.0 was used. Frequency and percentage was also used.

Statistical analysis

Statistical package for social sciences was used to analyse the data. Descriptive statistic including frequencies and percentage was used to analyse socio economic data and standard deviation was used to analyse anthropometry measurement of the children.

Results

Personal data of the under five

Table 1 showed the personal data of the under-five. One hundred and twelve (44.8%) under five were males while 138 were females (55.2%). About 209 (83.6%) were from Imo state while 41 (16.4%) were from other states of the country. Majority 240 (96%) were of the Igbo ethnic group, 1 (0.4%) Yoruba, and 4 (1.6%) Hausa. Five (2%) of the respondents were between the ages of 6 to 12 months, 114 (45.6%) were aged between 1 to 3 years, and 130 (52%) were aged 3 to 5 years (Table 1).

Socio-demographic data of the respondents

The socio-demographic data of the respondents showed that the 70 (28%) of the respondents’ fathers were civil servant, 94 (37.6%) were traders and 27 (10.8%) were farmers. Fifty (20%) of the respondents’ mothers were civil servants, 134 (53.6%) were traders and 25 (10%) were farmers, while 41 (16.4%) were of other occupations. Monthly income distribution of the children’s parents showed that 29 (11.6%) earned ₦10,000 – 50,000, 119 (47.6%) earned ₦50,000 – 100,000, 96 (38.4%) earned above ₦100,000, while only 6 (2.4%) earned a million plus. Data on the number of siblings the children have showed that 17 (6.8%) have one, 55 (22.0) have two, 92 (36.8%) have three, while others 86 (34.4%) have more than three. Data from living condition showed that 154 (61.6%) live in a bedroom flat, 44 (17.6%) live in one room apartment, 39 (15.6%) live in public yard, and 13 (5.2%) live in other kind of houses (Table 2).

Dietary practices of the respondents

Data on the dietary practices of the children’s care givers showed 221 (88.4%) prepared food at home to feed the children, while 29 (11.6%) purchased food outside the home. Majority of the children (78.4%) eat three times in a day, 15 (6.0%) eat twice daily, only 9 (3.6%) eat once in a day and 30 (12.0%) eat more than three times per day. Two hundred and fourteen (85.6%) took in-between meals, while 36 (14.4%) did not. Data on the choice of in-between meals showed that 173 (69.2%) took snacks, 28 (11.2%) took beverages, 22 (8.8%) took a full course meal, while 27 (10.8%) took other things as in-between meals. About 243 (97.2%) consumed fruits and vegetables, and 7 (2.8%) did not. One hundred and thirty eight (55.2%) consumed fruits and vegetables frequently, 66 (26.4%) twice in a week, 36 (14.4%) occasionally and 7 (2.8%) rarely (Table 3).

Food frequency of the respondents

Data from the frequency of food consumption from various food groups showed that 97 (38.8%) of the children consumed cereals and their products on a daily basis, 92 (36.8%) consumed cereals 3 to 4 times in a week, 33 (13.2%) once to twice weekly, 20 (8.0%) twice to three times monthly, and only 8 (3.2%) once in a month. Starchy roots and tubers consumption showed that 98 (39.2%) consumed roots and tubers three to four times weekly, 88 (35.2%) once to twice weekly, 48 (19.2%) daily, 11 (4.4%) two to three times per month. One hundred and seven (42.8%) consumed legumes and its products once to twice weekly, 83 (33.2%) three to four times weekly, 27 (10.8%) daily, 19 (7.6%) two to three times per month, and 14 (5.6%) once in a month. Data on vegetables consumption showed that 119 (47.6%) consumed vegetables daily, 72 (28%) three to four times weekly, 35 (14%) once to twice weekly, 14 (5.6%) two to three times per month, while only 10 (4.0) consumed vegetables once in a month. Eighty two (32.8%) consumed fruits once to twice per week, 79 (31.6%) daily, 59 (23.6%) three to four times per week, 23 (9.2%) twice to thrice monthly, and only 7 (2.8%) once in a month. 96 (38.4%) of the children consumed nuts and seeds two to three times monthly, 74 (29.6%) consumed one to two times in a week, 37 (14.8%) three to four times weekly, 23 (9.2%) twice to three times, and only 20 (8.0%) daily. Eggs, meat and poultry consumption showed that 95 (38%) consumed eggs, meat and poultry three to four times weekly, 93 (37.2%) daily, 48 (19.2%) 0nce to twice weekly, 11 (4.4%) two to three times per month and 3 (1.2%) once in a month. Eighty seven (34.8%) consumed beverages daily, 84 (33.6%) three to four times weekly, 54 (21.6%) one to two times weekly, 13 (5.2%) two to three times per month, and 12 (4.8%) once in a month. Data on milk and milk products consumption showed that 92 (36.8%) consumed vegetables three to four times weekly, 62 (24.8%) daily, 41 (16.4%) once to twice weekly, 33 (13.2%) two to three times per month, while only 22 (8.8%) consumed milk and milk products once in a month (Table 4).

Nutritional status of the under 5 children by sex

Table 5 showed the nutritional status of the under-five children. The weight for age of the children showed that 7 (2.8%) were wasted, 175 (70.0%) were normal or at low risk and 68 (27.2%) were slightly above normal. The height – for – age, status showed that 8 (3.2%) were stunted, 192 (76.8%) were normal or at low risk, while 50 (20%) were above normal. For weight for age, 4 (1.6%) were underweight, 200 (80.0%) were normal or at low risk, while 46 (18.4%) were above normal. The mid-upper arm circumference measurement showed that only 3 (1.2%) of the children were malnourished, 5 (2.05%) were at risk, while 242 (96.8%) were normal (Table 5).

Table 6 presents the mean and standard deviation for anthropometric measurements of the children. The mean height of the under-five children was 1.02±0.09 for the males and 1.02±0.08 for the females. The mean weight of the under-five children was 16.51±3.48 for the males and 17.01±2.79 for the females. The mean mid-upper arm circumference of the under-five was 15.15±2.12 for the males and 15.36±1.87 for the females (Table 6).

Discussion

Personal and socio-demographic data of the under five

Data obtained from the research showed that children aged 6 to 59 months were studied, of which 112 (44.8%) were males while 138 (55.2%) were females. Majority, 209 (83.6), of the respondents were indigenes of Imo State where the study was carried out and are Igbos 240 (96.0%). A greater percentage of the respondents aged 3 to 5 years 130 (52.0%). About 37.6% of the respondents fathers were traders, 28% were civil servants and 23.6% represented other occupational distribution. The high percentage of traders in the study revealed that trading is the major occupation of the fathers in the geographical location of the study. Similar trend was repeated among mothers of which 53.6% where traders, and 20% were civil servants. According to Mosley and Chen (2014) [3], maternal education affects children’s health and nutritional outcomes through its effect on improving women’s socioeconomic status. A higher level of maternal education leads to increased knowledge about health and nutrition, which, in turn, leads to an increase in the quality of the diets consumed by children [4]. If maternal education is to play a significant role in reducing child malnutrition, women need to be educated beyond the primary school level. Monthly income distribution of the respondents’ parents showed that a greater percentage earned between ₦50,000-100,000 which corresponds with recent study by Olodu et al. (2019) [5] on a higher monthly income more than ₦20,000, while 38.4% earned above ₦100,000. This is in accordance with reports by Mathieson and Koller, (2016) [6] who stated that healthy eating habits are largely determined by social, economic and cultural factors (such as place of residents) that influence access, availability and uptake. The number of siblings the respondents had gave a little insight on the probable family size of the respondents. Smaller family sizes (one 6.8%, two 22.0% and three 36.8% siblings) could be exposed to better care and access to healthy foods and adequate diet which can promote good health and reduce risk of diseases [5]. More than half (61.6%) of the respondents live in better houses which indicates good hygiene and sanitation, better living conditions and less overcrowding. Akombi et al. (2017) [7] reported that children from poor households are at a greater risk of being stunted and severely stunted than children from richer households. This may be attributed to the fact that with less income to spend on proper nutrition, children from underprivileged households are more prone to growth failure due to in-sufficient food intake, higher risk of infection as well as lack of access to basic health care services. Present study is supported by a study carried out in Zambia where children from poorer households reported a lower nutritional status than those from richer households [8]. Therefore, to improve child health in poor households, an establishment of properly functioning economic and financial structures which supports children from underprivileged households is needed so as to improve food security and access to basic health care services. The child’s well-being is affected by his/ her environment (including the home) which is largely influenced by the family structure, composition and relationship to members in the household [9].

According to WHO (2018) [10], Brazil experienced a sharp reduction of socioeconomic inequalities from 1996 to 2007 which resulted in child stunting dropping from 37% in 1974 to 7% in 2006–2007. Two thirds of the decline could be attributed to improvements in maternal schooling, family purchasing power, maternal and child health care, and coverage of water supply and sanitation services [11]. More girls were enrolled in and completed primary school in the 1990s which increased overall maternal schooling in adulthood. As a result of the education received, the women also had fewer children. The purchasing power of, and the minimum wage received by, unskilled workers increased, unemployment decreased, and cash transfer programmes for low-income families were expanded. Sanitation services also increased and severe food insecurity was reduced by 27% between 2004 and 2006–2007. Thus, income redistribution and universal access to education, health, water supply and sanitation services impacted child nutrition [11].

Dietary practices of the respondents

Data on the dietary practices of the children’s care givers showed 221 (88.4%) prepared food at home to feed the children, while 29 (11.6%) purchased food outside the home. Food is the fuel necessary to get through a normal day. Calories in food provide energy to carry out regular day-to-day activities. Without an adequate amount of this energy, pupils may fall asleep in school or lack the energy to pay attention to an entire day of classes [12]. Home prepared meals are better and more hygienic for a growing child since adequate food condiments are added and there is a regulated rate of seasoning and processed ingredients going into the food [12]. It is also healthier and cheaper than purchased meals from fast foods. Greater percentage (78.4%) of the respondents observed the routine three square meal per day, while 12.0% east more than three times daily. Regular eating practices and healthy food choices ensure individuals meet their nutritional requirements for growth and health maintenance [8]. About 85.6% had in-between meals, of which 69.2% had snacks, 11.2% had beverages and 8.8% had a full course meal. According to Gregory et al. (2010) [13] the consumption of snacks is a worldwide issue among children and adolescents regardless of where they live, whether in urban or rural areas or in developed or developing countries. However, snacking is a key characteristic of a children’s diet, and it is not a bad practice on its own. Snacks, if chosen wisely, can contribute positively to nutrient intake. In another study, Hackett et al. (2007) [14] opined that snacks should provide one fourth to one third of the daily energy intakes for children [14]. Majority of the children (97.2%) had access to fruits and vegetables, with about 55.2% on frequent consumption of fruits and vegetables, while 26.4% consumed twice weekly. This showed that their mothers are aware of the benefits of micronutrients to their baby’s foods.

Food frequency of the respondents

Table 4 showed the frequency of food consumption of the respondents. A greater percentage, 36.8%, consumed cereals and cereal products on a daily basis. This showed that cereals constitutes the bases of food consumption of the respondents. Maize pap is one of the major cereal incorporated as complementary feeding and given to babies at 6 months of age by individuals of low socio-economic strata. Most times, milk, soybean, boiled eggs and/or sugar are added to enhance the nutrient content of the food. Other cereal based complementary foods included Cerelac and SMA gold. The children are also introduced to foods eaten at home that normally go down well with the cereal, such as beans, moi-moi and akara with pap, rice; jollof, white with stew etc. These meals contain higher energy than the infant formular and help get the children acquainted with the meals prepared at home. Another food group mostly consumed by the children was starchy roots and tubers, evidenced by 39.2% on a consumption basis of three to four times weekly. Roots and tuber crops mainly consumed are mashed potatoes, yam, pounded yam and cassava products such as semovita etc. Some low income families introduce garri to their children which is normally cooked until it gels and given with soups such as okro, ogbono and vegetable soups. Cereals and starchy roots and tubers provide the needed energy for daily activities. Previous study by Ajao et al., (2012) [15] on influence of family size, household food security status, and child care practice on nutritional status of under- five children in Ile-Ife, Southern Nigeria showed that the energy food and body building food forms the bulk dietary intake (45% and 38% respectively) while protective and refined foods were consumed in small quantity (about 8% and 9%).

Legume products are consumed by almost half of the respondents (42.8%). They contain protein of low biological value which are also essential for growth and development of the young child. The most frequently consumed legumes were beans and soybeans. Soybeans contain protein of low biological value and it is being added to pap, cerelac and other formular for the children. Beans were also consumed mainly in mashed beans porridge, akara, moi-moi, and boiled rice with beans. Beans, groundnuts and soya beans are good sources of protein and cheaper than animal products. The respondents purchased more of these as a result of their poor socio- economic status and the rigid economy of the nation. A second reason is that soybean has a variety of usage and is regarded as the “magic food”. Previous studies reported that children consume vegetables mostly in soups and stew prepared at home than in-between meals [12]. With respect to vegetables, tomatoes, onion, pepper, green leafy vegetable, garden eggs and okro were consumed on a daily basis by almost all the respondents mainly in soups, stews and sauces as accompaniments to staple dishes like wheat meal, gari, cooked cereals, tubers and plantains.

Fruits and vegetables are good sources of vitamins, minerals and fiber. Vitamins help to build the body’s immune system in order to fight diseases and infections. They also assist metabolism of nutrients and can be converted to amino acids for use by the body (niacin to tryptophan). Watermelon, pineapple, banana and pawpaw were consumed by respondents on weekly basis. Because some fruits are seasonal, mangoes, avocado pear and local pear were consumed occasionally. The children consumed fruits regularly because of the knowledge of its nutritional benefits their mothers possessed. Frequency of nuts and seeds consumption showed that the children consumed lesser quantities throughout the week, evidenced by only 8.0% daily consumption, 14.8% three to four times weekly and 29.6% once to twice weekly. Nuts contain omega 3 fatty acids which help in brain development, and for healthy blood vessels.

The responses obtained from eggs, meat and poultry revealed that eggs, meat, and frozen fish were the main sources of animal protein consumed daily by most of the children. This is evidenced by a consumption rate of 38.0% three to four times weekly and 37.2% on a daily basis. These were mainly consumed in soups, stews, rice as well as eggs used in preparing breakfast for the children and lunch packs in school. Eggs, meat and poultry are good sources of protein of high biological value. They are good for growing children since they contain the essential amino acids needed for good health. One hundred and eight (43.2%) of the respondents consumed fish and fish products on a daily basis, 84 (33.6%) three to four times weekly and 17.2% once to twice every week. This is quite encouraging since fish is one of the most important protein sources in our diet. It contain both omega 3 and omega 6 fatty acids which help to combat pro inflammatory substances such as cytokines, prostaglandins and the eicosanoids.

The response obtained from milk and milk products consumption showed that 24.8% consumed milk products daily, 36.8% three to four times weekly and 16.4% once to twice in a week. This is quite encouraging and could be attributed to the fact that there is adequate knowledge of the nutritional benefits of milk. Secondly, the economic condition of the families were high which made it possible to provide such for their children. Most of the milk consumed by the children below 12 months were Peak 123, Pre-Nan and Nutri Start 2. Among the fats and oils, palm oil and refined vegetable oils were the most frequently consumed. About 79.2% of the children consumed fat and oil products daily. This is encouraging since fats improve the palatability of food, improves heart health and contributes the highest energy in the body. Palm oil was used mainly in soups and also served as an accompaniment to cooked beans. This is encouraging since palm oil is a rich source of pro-vitamin A which is crucial for vision and maintaining healthy cells, especially skin cells.

Nutritional status of the under 5 children by sex

Child malnutrition occurs when a child’s intake of nutrients (fat, protein, vitamins and minerals, etc.) is insufficient to sustain the needs of her body. Childhood malnutrition persists as a public health problem in developing countries. It is estimated that less than 5% of children in developing nations are wasted [16]. The main factors associated with stunting in the study were: sex of the child, wealth index and geopolitical zone. Akombi et al. (2017) [7] reported that the factors associated with severe stunting included: sex of the child, wealth index, geopolitical zone and maternal BMI. In this study, we observed that male children had a significantly higher risk of being stunted and severely stunted than their female counterpart. The prevalence of wasting in the current study is a little above this estimate. The current study indicates that 8% of the study population was stunted and this falls within the WHO estimate for developing countries [16]. The prevalence of underweight, stunting, and wasting from this study is lower than what was reported by Manjunath et al. (2008) [17]. It is also consistent with the estimate from the 2013 national demographic and health survey, except for stunting [18]. Stunting in this population is lower than the national estimate. Stunting and underweight in the current study is slightly lower than the prevalence in South Eastern Nigeria. However, the prevalence of wasting reported by Ezeama et al. (2015) [19] (18.1%) from south eastern Nigeria is higher than prevalence in the study population (7%). The Government should sustain and scale up existing interventions that will reduce malnutrition. Prevalence of PEM is 1.2%. This is lower than the prevalence reported by Andy et al. (2016) [20].

Several factors are associated with PEM and vary from place to place. According to Andy et al. (2016) [20], the prevalence of PEM among male children is higher than in female children and the relationship between PEM and gender is statistically significant. This finding is similar to that obtained from the present study and the position of Ubesie et al., (2012) and Yalew (2014) [21,22]. This underlines the need to give special attention to mothers of male children when counselling women about the nutrition of their children. This gender based health inequality may be as a result of community specific cultures in Nigeria which reflect a historical pattern of preferential treatment of females due to the high value placed on women’s agricultural labor [23]. Also, male children tend to be more physically active and expend large amounts of energy which should have been channelled into increasing growth. On the other hand, females are culturally expected to be less active and stay at home with their mothers near food preparation. This finding is consistent with results from other cross-sectional studies carried out in Kenya [24], Tanzania [25] and Ghana [26]. In Jayatissa (2012) [27] study on assessment of nutritional status and associated factors; there were no consistent differences between sexes regarding occurrence of stunting but a higher prevalence of wasting and underweight was seen among males. The MUAC also shows that 1.78% males and 0.72% females were malnourished. Akorede and Abiola (2013) [28] stated that since the present condition (nutritional status) have a lot of effect on the future then adequate care should be given to the children at that tender age [29-36]. The best way to achieve optimal nutritional status is to improve on the socioeconomic conditions of children and teach nutrition education to mothers, most especially on the best practices to care for their children.

Conclusion and recommendation

This study shows that stunting, underweight and wasting results from a complex interaction of factors. Hence at the individual level, interventions to prevent stunting, underweight and wasting should focus on improving women’s nutrition and education to reduce low birth size, improve household hygiene and promotion of appropriate complementary food and feeding practices. Poor Socioeconomic and environmental conditions are important determinants of nutritional status. Educated and employed mothers have control over the purchase of the dietary items and will be more qualified and capable of taking care for their children properly. Mothers should be adequately educated on how best to imbibe nutrition knowledge to the care of their baby so as to reduce child malnutrition in Imo State. Education of women should be treated with utmost priority because it will help raise the standard of living of the family and pave way for a better socio-economic status. Government and nutrition policy makers should enact policies that will enhance food security, and promote programs like operation feed the nation, food bank and cash remission. Further research can be carried out on the above study, more especially in the Northern parts of the country where child malnutrition has wrecked much havoc.

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Tuesday, 25 May 2021

Iris publishers-Global Journal of Nutrition & Food Science (GJNFS)

 

Contamination Status of Polycyclic Aromatic Hydrocarbons (PAH s) In Atmospheric Particulate Matter PM2.5 Samples of a Semi-Residential Area of Dhaka, Bangladesh

Authored by YN Jolly*

Abstract

This study deals with the determination of the polycyclic aromatic hydrocarbons (PAHs) in the atmospheric particulate matters (PM2.5) at a semi residential site of Gazipur, Dhaka, Bangladesh. Source identification and possible human health impact of polycyclic aromatic hydrocarbon was evaluated as well. A total of 20 samples were collected in six weeks period of time. Polycyclic Aromatic Hydrocarbons (PAH’s) were determined using gas chromatography-mass spectrometry. The average concentration of Anthracene, Phenanthrene, Pyrene, Chrysene, Benzo (a) anthracene, Benzo(a)pyrene, perylene were found to be 0.309, 0.159, 0.227, 2.120, 1.954, 2.269 and 3.373μgm-3 respectively. Two-way ANOVA test revealed that the concentration of different PAHs species (Fcal> Fcrit) are significantly different from each other at a 95% confidence level. The main contributory sources for PAHs were found gasoline exhaust, diesel exhaust, wood burning and brick kilns. The result revealed that these compounds are present in a higher level in the atmosphere when compared with the value of other countries in the world. Concentration of highly carcinogenic Benzo(a) pyrene was in a range where carcinogenic effect is an immediate threat in case of long-time exposure and hence regular monitoring is suggested.

Keyword: Polycyclic Aromatic Hydrocarbon; Air-Metrics Mini-Vol Samplers; Gas Chromatography-Mass Spectrometry; Quartz Filters

Introduction

Polycyclic aromatic hydrocarbons (PAHs) are organic compounds consist of two or more fused benzene rings in a linear or cluster arrangement, typically found as a complex mixtures [1]. They are very stable organic pollutants that are made up of only carbon and hydrogen and occur naturally but, they can be synthesized as individual compounds for research purposes. Furthermore, they have high boiling and melting points with high molec ular weights and are able to survive at high temperatures from the combustion of fuel from automobiles and airplanes engines and most of them have low water solubility [2]. Polycyclic aromatic hydrocarbons (PAHs) are considered ubiquitous in the environment and can be formed from either natural or manmade combustion sources [3]. The dominant sources of PAHs in the environment are thus from human activity: wood-burning and combustion of other bio-fuels etc., and wildfires are another notable source. Dungor crop residues contribute more than half of annual global PAHs emissions, particularly due to bio fuel use in India and China (Anita and Maharaj,2004), industrial processes and the extraction and use of fossil fuels made up slightly more than one quarter of global PAHs emissions, dominating outputs in industrial countries such as the United States. Lower-temperature combustion, such as tobacco smoking tends to generate low molecular weight PAHs, whereas high-temperature industrial processes typically generate PAHs with higher molecular weights [4].

Atmospheric PAHs are distributed (Figure 1) between the gas and particulate phases depending on their physicochemical properties. They can be transported through the atmosphere over long distances. Polycyclic Aromatic hydrocarbons are emitted into the atmosphere either as vapors or associated with primary aerosol particles. Once enters in the atmosphere, the residence times and ultimate fates of these semi volatile chemicals depend upon their distributions among vapor, particle, and droplet phases. The atmospheric chemical and photochemical reactions of PAHs are of great importance because the decomposition product of the PAHs may be more hazardous to human health than the PAHs from which they were derived [5]. A number of experimental studies have demonstrated that many PAHs are susceptible to photochemical and/or chemical oxidation under simulated atmospheric conditions [6]. Nitro PAHs are emitted as a result of incomplete combustion processes.

PAHs have been linked to different cancers in well-established animal model studies [7]. The structure of a PAH influences whether and how the individual compound is carcinogenic [8]. Some carcinogenic PAHs are genotoxic and induce mutations that initiate cancer; others are not genotoxic and instead affect cancer promotion or progression [9] and hence continued research regarding the mutagenic and carcinogenic effects from chronic exposure to PAHs and metabolites is needed. Other than carcinogenic, adult exposure to PAHs has been linked to cardiovascular disease as well [10]. PAHs are among the complex suite of contaminants in tobacco smoke and particulate air pollution and may contribute to cardiovascular disease resulting from such exposures [11]. laboratory experiments, animals exposed to certain PAHs have shown increased development of plaques (atherogenesis) within arteries [12]. Oxidative stress following PAH exposure could also result in cardiovascular disease by causing inflammation, which has been recognized as an important factor in the development of atherosclerosis and cardiovascular disease [13,14]. Biomarkers of exposure to PAHs in humans have been associated with inflammatory biomarkers that are recognized as important predictors of cardiovascular disease, suggesting that oxidative stress resulting from exposure to PAHs may be a mechanism of cardiovascular disease in humans [15]. Multiple epidemiological studies of people living in Europe, the United States, and China have linked in uterus exposure to PAHs, through air pollution or parental occupational exposure, with poor fetal growth, reduced immune function, and poorer neurological development, including lower IQ.

As PAHs are known to have carcinogenic, mutagenic and teratogenic properties, their persistence in the environment have been placed them on the list of priority pollutants by the United States Environmental Protection Agency (US-EPA) and also the European Environment Agency [16]. People from all over the world are concerned more about the air pollution aspects due to the increased rate of mortality and morbidity and also multifarious effects of particulate pollution and we are not out of it. In this regard it is imperative to have a systematic study ascertaining the facts concerning the nature, sources, and trends of the particulate pollution in our beloved city, Dhaka, Bangladesh.

Gazipur area of Dhaka, Bangladesh is known to have moderately dense in population with high traffic and other industrial establishments like garments factories etc. There are several brick kilns in and around the area; more over there is a very busy rail station. Different types of industrial and regular activities are there responsible to contribute a lot carcinogenic aromatic polycyclic hydro carbons in the air of that area that ultimately affects local habitants as well as the visitors. Present study therefore sketched to determine the polycyclic aromatic hydrocarbon concentration in the atmospheric particulate matters collected from Gazipur, Dhaka, Bangladesh, identification of possible sources and human health impact. The main objectives are therefore:

• Determination of the polycyclic aromatic hydro-carbons concentration in the atmospheric particulate matters of Gazipur air

• Identification of the source of the polycyclic aromatic hydrocarbon in the atmosphere.

• Understanding the possible human health impact of polycyclic aromatic hydrocarbon.

Materials and Methods

Sampling site

Air samples were collected from Gazipur area of Dhaka, Bangladesh, which is a residential area of moderate population density. The sampling location is within 20 m from a local road and about 200m from a secondary roadwith moderate traffic density. The highway of Joydeb puris a very busy traffic point, which is about 5 km west to the studied site. Joydebpur rail station, through which daily 60 trains pass away, is about 100m away from the sampling location. At “Konabari” and “Kodda” which are about 5 to 7 km to the north-west of the sampling site, more than 100 brick kilns are there in production using kindle wood. There are also many garments and other industrial units at 4 to 7 km distance from this site (Figure 2).

Samples collection and preparation

PM2.5 (particulate matter) sampling was started from 13 January 2014 by Air-Metrics Mini-Vol samplers at Joydebpur (Gazipur), Dhaka, Bangladesh. And the samplers were placed on the flat roof of the continuous air monitoring station (CAMS-4) site of Clean Air and Sustainable Environment (CASE) project, Gazipur city corporation central symmetry, at 20 feet height from the ground level. The amount of air passed was maintained at 7.2m3.PM2.5 was collected simultaneously for every 24 hours (from 10 a.m. to 10 a.m. of the next day) at the sampling site. The pre-weighted conditioned clean filters (quartz) were loaded to respective filter holder assembly at the conditioning room of CAMS. After sampling, filter holder assemblies (keeping the exposed filters inside) were brought to the conditioning room of the Atomic Energy Centre (AEC), Dhaka, directly from the sampling site for conditioning and PM filter retrieval. Special care was taken in transporting the exposed filter holder assemblies, so that there should be no PM loss.PM2.5 masses were measured in the Atmospheric and Environmental Chemistry Laboratory of Chemistry Division of the Atomic Energy Centre (AECD), Dhaka and preserved under 4°C temperatures. The aerosol sample having PM2.5 was determined by weighing filter before and after exposure using a micro balance. The difference in weights for each filter was calculated and the mass of each PM2.5 sample thus determined.

Extraction of Samples

The particulate PAHs containing sample was weighed and taken into the volumetric flask, then about 30 ml dichloromethane (DCM solvent solution) was added to dissolve the PAHs, kept for 24 hours then sonicated. After sanitations the extract was filtered through what man filter paper and collected in a clean volumetric flask. Special attention was given to avoid loss of extract. Silica clean up column was prepared and the samples were passed through the column and collected. The total solution was concentrated using liquid nitrogen gas to 1-2 ml and transferred into a GC vial for analysis.

Preparation of standard PAHs solution

A known amount of PAHs was dissolved in definite amount of solvent (dichloromethane) to prepare 5 ppm PAHs standard solution of Phenanthrene, Anthracene, Pyrene, Chrysene, 1.2-benzanthracene, Perylene, Benzo-a-pyrene, marked with individual identification number and was stored in the refrigerator. The quantitative determination of PAHs has been done by external calibration curve method. The calibration curve of each compound is prepared with known concentrations of the compound prepared and run through GC-MS. Standard curve for each compound is generated by plotting the area vs. the concentration range for corresponding samples. Over this concentration range, the linear regression analysis of peak areas (y) in function of concentration (x), calculated by least square method. Calibration curve for each compound is presented in (Figure 3).

Chromatogram of a standard PAHs solution

The GC column temperature program employed was 400C to 2800C, started from 400C with holding time 1 min and then raised to 1600C at 100C min-1 ramping and finally the temperature raised to 2800C at 150C min-1 ramping. The injector and detector temperature were 2500C and 2800C respectively. The difference in the chemical properties between different molecules in a mixture and their relative affinity for the stationary phase of the column will promote separation of the molecules as the sample travels the length of the column. The molecules are retained by the column and then elute come off from the column at different time (called the retention time), and this allows the mass spectrometer downstream to capture, ionize, accelerate, deflect, and detect the ionized molecules separately. The mass spectrometer does this by breaking each molecule into ionized fragments and detecting these fragments using their mass-to-charge ratio. So, the components have been separated and detected through their retention time and quantified the area through their charge to mass ratio. The retention time of standard solution is 21.59, 21.75, 25.79, 29.40, 29.51, 33.23 and 33.45 min for Phenanthrene, Anthracene, Pyrene, Chrysene, Benz[a]anthracene, Perylene, Benzo[a]pyrene respectively.

Result and Discussion

Analysis of different PAHs in PM2.5 samples

Distribution of different PAHs revealed that the concentrations vary from time to time depending on the trend of air flow. In general, concentration of total PAHs is easily affected by location and seasonal variation. Besides local sources of PAHs, in both urban and rural areas, transport of PAHs through atmosphere can play a large role. The highly carcinogenic benzo[a]pyrene was normally found in the range of 1-20 ng/m3 in Europe, and around 1 ng/m3 in the USA. For other PAHs, individual concentrations were generally in the range of 1-50 ng/m3 in Europe, 0.1-1 in North and South America and in Australia, 1-10 in Japan, and 10-100 in two towns in India and New Zealand [17]. The measured concentration of Phenanthrene, Anthracene, Pyrene, Chrysene, 1,2- Benzanthracene, Perylene, Benzo-a-Pyrene are presented in (Table 1).


Benz [a] anthracene

Benz [a] anthracene or benzo [a] anthracene is a polycyclic aromatic hydrocarbon with the chemical formula C18H12. According to scientists, more than 20% of the carbon in the universe may be associated with PAHs, possible starting materials for the formation of life. Benzo [a] anthracene is a constituent of tobacco smoke [17]. There was a dose-dependent decrease in cell density was observed due to exposure of benz (a)anthracene.

In the present study the average concentration of Benzo(a) pyrene in the atmospheric particulate matter (PM2.5) was found 2.26μg/m3. The highest concentration was found 6.682μg/m3 and lowest concentration was 0.009μg/m3 (Figure 4). The strongly carcinogenic benzo[a]pyrene was typically found in the range of 1–20 ng/m3 in Europe and around 1 ng/m3 in the USA [18]. Present study reveals the mean concentration of Benzo[a]pyrene is 2.269 μg/m3, which is almost 22 times more from India and 100 times more than from Europe [18] and which may be the result of incomplete combustion of organic matter at temperatures. The other sources may be residential wood burning, automobile exhaust fumes (especially from diesel engines) as the sample location is within a heavy traffic area. [19] Reported, after long-term inhalation of “pure” Benzo [a] pyrene at a concentration of 10ng/m3, cancer of the respiratory tract occurred in 35% of golden hamsters. The range of unit lifetime risks calculated from a number of selected Benzo[a]pyrene studies included in a meta-analysis was 1.1 × 10-3 to 4.8 ×10-3μg/m3. Some other risk estimates of respiratory tract cancer related to Benzo[a] pyrene in the ambient air have been calculated by the US Environmental Protection Agency and the estimated risk per year ranged from 0.11 × 10-5 to 1.4 × 10-5 per ng of Benzo[a]pyrene per m3(EPA Report No. EPA-450/5-83-006, 1984).





Phenanthrene

Phenanthrene is composed of three fused benzene rings and in its pure form, it is found in cigarette smoke, it is a known irritant, photosensitizing skin to light. Phenanthrene appears as a white powder having blue fluorescence. Phenanthrene is the backbone of morphinan, which in turn is the backbone of a large number of psychoactive chemicals including antitussives, analgesics, and dissociative drugs. Phenanthrene is absorbed readily from the gut and lungs. In general, these PAHs are highly lipid-soluble and pass across epithelial membranes.

In this study, the average concentration of Phenanthrene in the atmospheric particulate matters (PM2.5) was found 0.159μg/m3 with a highest concentration of 0.465μg/m3 and lowest of 0.039μg/ m3 (Figure 5). Phenanthrene is a rather common PAH. It occurs naturally in fossil fuels and is a product of incomplete combustion. The primary emission sources of phenanthrene are the combustion of fossil fuels but in this case it may be from traffic and exhausts from industry.

Anthracene

Anthracene is a solid polycyclic aromatic hydrocarbon (PAH) of formula C14H10, consisting of three fused benzene rings. Coal tar, which contains around 1.5% anthracene, remains a major source of this material. Anthracene, as many other polycyclic aromatic hydrocarbons, is generated during combustion processes. Exposure to humans mainly happens through tobacco smoke and ingestion of food contaminated with combustion products. Many investigations indicate that Anthracene is noncarcinogenic: “consistently negative findings in numerous in vitro and in vivo genotoxicity tests”. Furthermore, it is readily biodegraded in soil. It is especially susceptible to degradation in the presence of light [20]. The average concentration of Anthracene in the Gazipur air was detected 0.345μg/m3. The highest concentration was 0.903μg/m3 and lowest concentration was 0.025μg/m3 (Figure 6). The vast majority of anthracene is released to the environment when combustion is incomplete (usually because there is insufficient oxygen). In this case the possible source is emission from vehicle exhausts and domestic wood and coal fires. Emissions also arise from industrial effluents, municipal wastewater treatment facilities, waste incinerators and aluminum smelting.

Pyrene

Pyrene is a PAH with a molecular formula C16H10 and made up of four fused benzene rings, which results in a flat aromatic system. It is a colorless solid which is the smallest peri-fused PAH (one where the rings are fused through more than one face). It is formed during incomplete combustion of organic compounds. Pyrene was first isolated from coal tar, where it occurs up to 2% by weight [21]. Therefore, it is produced in a wide range of combustion conditions. Although it is not as problematic as benzopyrene, animal studies have shown that pyrene is toxic to the kidneys and the liver [21].

The average concentration of Pyrene was found in the gazipur air (PM2.5) was 0.227μg/m3. The highest concentration was 0.364μg/m3 and lowest concentration was 0.011μg/m3 (Figure 7). It is released to the environment through various waste streams. Some source of pyrene includes exhaust from motor vehicles, cigeratte smoke, coal, oil and wood burning furnaces. It is produced in a wide range of combustion conditions. For example, automobiles produce about 1μg/km [20].

Chrysene

Chrysene is a PAH with the molecular formula C18H12 and made up of four fused benzene rings. It is a natural constituent of coal tar, from which it was first isolated and characterized. It is also found in creosote, which is a chemical used to preserve wood. Chrysene is formed in small amounts during the burning or distillation of coal, crude oil and plant material [22]. However, high purity chrysene is colorless, the yellow color being due to the traces of its yellow-orange isomer tetracene, which cannot be separated easily [22]. Chrysene is a ubiquitous environmental contaminant that occurs as a product of the incomplete combustion of organic compound. Humans are exposed to chrysene by oral, inhalation, and dermal routes. Exposure occurs through the consumption of fruits and vegetables grown in areas with high soil or atmospheric concentrations of chrysene and from drinking or using water contaminated with chrysene. Meats, particularly those with high fat contents, contribute significant quantities of chrysene to the diet from the paralysis of fats during the cooking process. Foods smoked or cooked over open coals contain even greater concentrations.

In this study the average concentration of Chrysene in the atmospheric particulate matters (PM2.5) was found 2.120μg/m3. The highest concentration was 7.533μg/m3 and lowest concentration was 0.100μg/m3 (Figure 8). It is a natural constituent of coal tar. Chrysene is estimated to have only about 1% of the toxicity of benzopyrene. It is also found in creosote at levels of 0.5-6 mg/kg [23].

1, 2-Benzanthracene

1, 2-Benzanthracene is a PAH with a molecular formula C18H12, is available as colorless to yellow brown fluorescent flakes or powder. It is stable, combustible, and incompatible with strong oxidizing agents. On decomposition, 1,2-benzanthracene releases carbon monoxide, carbon dioxide, acrid smoke, and fumes. During work, 1,2-benzanthracene can be absorbed into the body of occupational workers by inhalation, through the skin, and by ingestion. Exposures may cause irritation to the eyes, skin, and respiratory tract. Exposures to 1,2-benzanthracene is known to cause kidney damage.

The average concentration of 1,2-Benzanthracene was found in the atmospheric particulate matters (PM2.5) 1.954 μg/m3. The highest concentration was 7.736μg/m3 and lowest concentration was 0.019μg/m3 (Figure 9). The major source may be gasoline and diesel exhaust. Benz (a) anthracene is a carcinogenic constituent of tobacco smoke [24].

Perylene

Perylene or perilene is a polycyclic aromatic hydrocarbon with the chemical formula C20H12, occurring as a brown solid. It or its derivatives may be carcinogenic, and it is considered to be a hazardous pollutant. In cell membrane ecyto chemistry, perylene is used as a fluorescent lipid probe. Perylene are formed during the incomplete burning of coal, oil, gas, wood, garbage, or other organic substances, such as tobacco and charbroiled meat. Perylene did not induce mutations in cultured human lymphoblastic cells. Perylene exerted a cytotoxic effect on human keratinocytes in vitro. The agent is not classifiable as to its carcinogenicity to humans. The average concentration of Perylene in the present study was found 3.374μg/m3. The highest concentration was 11.229μg/m3 and lowest concentration was 0.155μg/m3 (Figure 10)

ANOVA test also revealed (Table 2) that the concentration of different PAHs species are significantly different (Fcal> F crit) at different sampling times, which indicated that concentration of PAHs species are correlated with times and seasons. Two-way ANOVA test revealed that the concentration of different PAHs species (Fcal> F crit) are significantly different from each other at a 95% confidence level. ANOVA test also revealed that the concentration of different PAHs species are significantly different (Fcal> F crit) at different sampling times, which indicated that concentration of PAHs species are correlated with times and seasons.




Pearson’s Correlation

The Pearson’s correlation matrix between all the variables (e.g. Benzo(a)Pyrene, Phenanthrene, Anthracene, Pyrene, Chrysene, 1,2- Benzanthracene and Perylene) in air particulate matter PM2.5 samples was performed using a windows version software ‘IBM SPSS Statistics 20’ (IBM, USA); and the results are presented in (Table 3). The study revealed a significant positive correlation between the Chrysene and Benzo (a) Pyrene, 1,2-Benzanthracene and Perylene; Benzo (a) Pyrene and Perylene; Anthracene and Phenan-threne; and 1,2- Benzanthracene and Chrysene at a 95% Confidence level -indicating they are coming from the same source/s. Reversely a negative correlation was also observed between Chrysene and Anthracene (-0.460*) at a 95% confidence level.

Conclusion

The average concentration of Benzo-a-Pyrene, Phenanthrene. Anthracene, Pyrene, Chrysene, 1,2- Benzanthracene and Perylene, were 2.26μg/m3 , 0.16μg/m3, 0.35μg/m3 , 0.23μg/m3 , 2.12μg/ m3 , 1.95μg/m3 , and 3.37μg/m3 respectively The most carcinogenic Benzo-a-Pyrene (BAP) was detected with a concentration of 2.26μg/m3 in Gazipur air but WHO guide line value for BAP is between 0.1 and 1.3 ng/m3 for Lung cancer. The strongly carcinogenic benzo[a]pyrene was typically found in the range of 1–20ng/ m3 in Europe and around 1ng/m3 in the USA but in our study it is 2.26μg/m3 which is almost 100 times more than that found in Europe and USA. Average concentration of seven PAHs of Gazipur area was 1.49μg/m3. Whereas the average concentrations of particle- bound PAHs were 0.27±0.16μg/m3 in North Chinese Plain and hence Gazipur air contains more than 5 times greater amount of PAH’s and is really alarming [25]. showed that average concentration of measured sixteen polycyclic aromatic hydrocarbons (PAHs) in total suspended particulate matter (TSPM) from an urban and industrial cum residential site in Agra (India) from December 2005 to December 2006 were 115±17ngm3 [26]. Also reported, average concentration of total PAH was extremely high, with annual average concentration of 155ng/m3 in air sample collected from the Kathmandu Valley in the foothills of the Himalayas. The average concentrations of particle-bound total PAHs were 267ng/m3 in North Chinese Plain. [27] And hence in the present study average total PAHs are 10.439μg/m3.

Due to the industrialization and modernization of society, the introduction of motorized vehicles, and the explosion of the human population, massive traffic, burning of fuel, burning of coal in the brick kilns and power plant, burning of different types of plastic, dust particles from the different construction sites were the sources of the PAHs in the Gazipur area. The concentration was found in a level where there is a potential threat to carcinogenic effect due to long time exposure. Therefore, it is essential to develop an air pollution abatement strategy to protect people from the hazardous effects arising from elevated atmospheric PAHs by the systematic study of air pollution. The Government of Bangladesh should take immediate action to reduce these high concentrations of PAHs [28].

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