Abstract
Bangladesh – one of the most densely populated countries of the world— has plentiful water sources, but these sources are being polluted continuously. Both surface water and groundwater sources are contaminated with different contaminants like toxic trace metals, coliforms as well as other organic and inorganic pollutants. As most of the population uses these water sources, especially groundwater sources which contain an elevated amount of arsenic throughout the country; health risk regarding consuming water is very high. Death due to water-borne diseases is widespread in Bangladesh, particularly among children. Anthropogenic sources such as untreated industrial effluents, improper disposal of domestic waste, agricultural runoffs are the main contributors regarding water pollution. A total water pollution status of this country, as well as the sources of this severe condition, is crucial to evaluate public health risk. For this purpose, we reviewed hundreds of well recognized international and national journals, conference proceedings and other related documents to draw a complete picture of recent water pollution status and its impact on public health; also the sources of water pollution are identified.
Keywords: Environmental health, Environmental pollution, Environmental risk assessment, Environmental toxicology, Public health, Water pollution, Bangladesh, Heavy metal pollution, Pesticides
1. Introduction
Why are we able to live in this planet? Why are other animals and plants allowed to live here? If we endeavor to find out the answer of these inquisitions, we may easily perceive that water is the spring of life. According to biologists, all life form came from the sea means water. We are living on this planet due to the blessing of water. From the dawn of civilization to till now, humans (cave dwellers to city dwellers) have been using water for various seminal purposes: drinking, bathing, watering animals, and irrigating lands. However, this limited resource means source of life under threat from the population, chiefly generated by human factors. Almost 71% of the earth's total surface is covered with water, only 2.5% of this amount can be considered as freshwater (Shiklomanov, 1993). At present, 1.6 billion of people are facing economic water shortage, and two-thirds of the world's population is experiencing water scarcity at least one month in a year (FAO, 2007; Mekonnen and Hoekstra, 2016). Recently scientists have found that 21 of the world's 37 largest aquifers around the world have crossed their sustainability tipping points (Richey et al., 2015). The condition of water stress and scarcity will be worsened. Almost 1.8 billion people living in various regions all over the world may face absolute water scarcity by 2025 (WWAP, 2012).
However, these limited water resources are under threat from the pollution, chiefly generated by human factors. The agricultural sector, industrial production, mining, power generation, and other factors are some of the contributors to the pollution of water bodies, which will eventually affect humans in general (UN-Water, 2001). Diseases: cholera, diarrhea, dysentery, hepatitis A, etc. are directly linked to the unhygienic and contaminated potable water. It is estimated that each year more than 842,000 people die from diarrhea globally (WHO, 2017a,b). Arsenic pollution is one of the major groundwater contaminations, and it affects nearly 70 million people worldwide (UNESCO, 2009).
Like the rest of the third world country, Bangladesh (Fig. 1), one of the most densely populated countries, is facing severe water pollution and scarcity. Although 97% of the total population has access to water, the quality of water is always questionable (WHO, 2018). Bangladesh is a riparian country, consisting of more than 230 large and small rivers (Figs. 2 and 3). But these rivers are now choked by the pollution caused by mainly human intervention (Majumder, 2009). Groundwater is not also safe as the threat of arsenic contamination is very high all over the country. 97% of the total population in rural areas depend on the tubewells for drinking water; as a result, 35 to 77 million people have been chronically exposed to arsenic in the first decade of the millennium (Flanagan et al., 2012). 8.5% of the total death in Bangladesh is caused by water, sanitation and hygiene-related issues (UN-Water, 2013).
Fig. 1.
Administrative map of Bangladesh [source: (Map, 2019)].
Fig. 2.
Rivers of Bangladesh [Source: (Banglapedia, 2019)].
Fig. 3.
Land usage of Bangladesh (Reddy et al., 2016).
Adequate knowledge about the pollution status of all the water sources is thus crucial for ensuring safe and hygiene potable water. A detailed country wide drinking water quality survey was conducted by Bangladesh Bureau of Statistics which was titled as ‘Bangladesh National Drinking Water Quality Survey’ (BNDWQS) of 2009 with the technical help from UNICEF. Samples were collected from 300,000 household sources in 15,000 randomly selected clusters around the country. The report suggested that 97.8 of the population were using safe drinking water and 13.4% of the samples exhibited a higher concentration of arsenic (Statistics, 2009). But various individual studies on smaller scale revealed the much severe condition of water pollution. The Department of Environment (DoE) of Bangladesh regularly monitor the surface and groundwater quality of the country. These year-long monitoring programs have shown the increasing pollution rates in rivers and other surface water sources over time (DoE, 2014).
The complete picture of overall water pollution situation of Bangladesh is of great importance from every perspective. In this paper, we have compiled the recent data in this regard. Hundreds of journal articles, conference proceedings, reports published by renowned organizations, books and other reliable national and international materials have been reviewed to extract meaningful information about the present pollution status which is then arranged and presented systematically. Furthermore, the impact of this pollution on the public health of Bangladesh is also discussed in detail.
2. Main text
2.1. Physicochemical properties of water sources
The physicochemical properties of water can influence the development of biological life form in water and subsequently can cause an impact on the quality of water (Soja and Wiejaczka, 2014). Physical properties such as temperature, turbidity, electrical conductivity and chemical properties for instance dissolved oxygen (DO), Biological oxygen demand (BOD), Chemical oxygen demand (COD), all come under this group.
Biological Oxygen Demand (BOD, or more specifically BOD5) can be used as an indication of the extent of organic pollution in the aquatic systems, which adversely affect the water quality (Jonnalagadda and Mhere, 2001). Though there is no guideline value of BOD set by WHO, Bangladesh Standard doesn't allow more than 0.2 mg/L BOD in drinking water. A very high value of BOD can be seen in heavily polluted surface water of Bangladesh. Many studies found the elevated value of BOD in water sources in Barapukuria, Dinajpur (Bhuiyan et al., 2010), Dhaka-Narayanganj-Demra (D.N.D) Embankment (Sultana et al., 2009), Buriganga river (Ahmed et al., 2011b). Chemical Oxygen Demand (COD) is also a very practical parameter in the determination of polluted water (Zuane, 1996). WHO didn't set any guideline value for COD, but Bangladesh Standard for COD is maximum 4 mg/L. Only one study calculated the COD value of groundwater which was slightly higher than the recommended value (Table 1). Dissolved Oxygen (DO) is also measured in water quality testing. For drinking water, Bangladesh Standard described its maximum allowable concentration at 6 mg/L. The maximum concentration DO (12.77 mg/L) was found in the surface water near Barapukuria coal mine area, Dinajpur (Bhuiyan et al., 2010). A high concentration of DO (above 12–14 mg/L) can cause ‘gas bubble disease’ in fishes of the water body (Puri & Kumar, 2012); whereas a low concentration of DO has a direct effect on the corrosion of water supply line pipe and psychological results for consumers (Zuane, 1996).
Table 1.
Physicochemical properties parameters in Bangladesh in surface water and groundwater. Data are extracted from various individual studies and arranged chronologically based on year of publication of the reviewed articles. Values given represent the mean values or mean values plus-minus standard deviation (S.D.), where the values with ± in the parenthesis () represents average ± S.D.
| Samples Location | BOD (mg/L) | COD (mg/L) | DO (mg/L) | Temperature (°C) | pH | TDS (mg/L) | Conductivity (μ-mhos/cm) | Reference |
|---|---|---|---|---|---|---|---|---|
| Surface Water | ||||||||
| Halda River | ─ | ─ | 6.874 | 27.02 | 6.72 | 66.32 | (Patra and Azadi, 1985) | |
| Surma River (Dry) | (1.00 ± 3.8) | (1.53 ± 0.52) | (5.52 ± 1.40) | ─ | (6.13 ± 0.29) | (139.30 ± 38.40) | ─ | (Alam et al., 2007) |
| Surma River (Monsoon) | (0.88 ± 0.31) | (1.34 ± 0.40) | (5.72 ± 1.42) | ─ | (6.09 ± 0.33) | (129.50 ± 37.44) | ─ | (Alam et al., 2007) |
| Mouri River | 21.268 | 348.275 | 5.537 | 23.23 | ─ | 283.5 | 176 | (Kamal et al., 2007) |
| Surface Water near D.N.D Embankment | (584.75 ± 249.66) | (1264.67 ± 534.86) | (0.84 ± 0.75) | (33.75 ± 1.71) | (8.70 ± 0.72) | (1369.33 ± 780) | (2076.58 ± 892.55) | (Sultana et al., 2009) |
| Sadar ghat, Buriganga River (Rainny Season) | ─ | 54.9 | ─ | 29.88 | 7.1 | ─ | ─ | (Saha et al., 2009) |
| Sadar ghat, Buriganga River (Winter Season) | 9.1 | 22.3 | ─ | 19.33 | 7.05 | ─ | ─ | (Saha et al., 2009) |
| Barapukuria, Dinajpur (Drainage Water) | 16.87 | 260.1 | 12.77 | 34.1 | 6.75 | ─ | ─ | (Bhuiyan et al., 2010) |
| Barapukuria, Dinajpur (Ground Water) | 19.9 | 233.9 | 9.82 | 30.2 | 8.85 | ─ | ─ | (Bhuiyan et al., 2010) |
| Buriganga River, Dhaka (Different Seasons) | 44.69 | ─ | ─ | ─ | ─ | 671.83 | ─ | (Ahmed et al., 2011b) |
| Katrnatoli River, Savar, Dhaka (Different Seasons) | 33.99 | ─ | ─ | ─ | ─ | 249.44 | ─ | (Ahmed et al., 2011b) |
| Ashulia, Dhaka | (0.89 ± 0.86) | (56.57 ± 27.13) | (4.72 ± 1.1.3) | (27.28 ± 1.80) | (7.47 ± 0.18) | (838.33 ± 374.47) | (983.25 ± 210.82) | (Bhuiyan et al., 2011) |
| Amin Bazar, Dhaka | (0.72 ± 0.65) | (50.01 ± 33.14) | (4.95 ± 1.28) | (28.00 ± 2.10) | (7.46 ± 0.19) | (673.33 ± 195.88) | (1100.33 ± 131.42) | (Bhuiyan et al., 2011) |
| Tejgaon area, Dhaka (Wet Season) | 17 | 130.5 | 0.1 | ─ | 7.1 | 303.1 | 852.7 | (Mondol et al., 2011) |
| Tejgaon area, Dhaka (Dry Season) | 0.5 | 104 | 0.2 | ─ | 7.1 | 483.3 | 835.9 | (Mondol et al., 2011) |
| Karatoa river | ─ | ─ | ─ | ─ | (7.28 ± 0.16) | (324.87 ± 107.55) | (Zakir et al., 2012) | |
| Shitalakshyaa River | ─ | 120 | ─ | 25.15 | 8.1 | 737.5 | 1087.5 | (Sikder et al., 2013) |
| Turagh River | ─ | 35 | ─ | 21.55 | 7.45 | 410.5 | 579.5 | (Sikder et al., 2013) |
| Bongshi River | ─ | 35 | ─ | 20.87 | 7.433 | 420.33 | 594 | (Sikder et al., 2013) |
| Turag river (2006) | 2.8 | 58 | 6 | ─ | 7.1 | 342 | 98 | (Banu et al., 2013) |
| Turag river (2010) | 22 | 102 | 0 | ─ | 7.5 | 812 | 1800 | (Banu et al., 2013) |
| Karnaphuli River, Chittagong (Summer) | ─ | ─ | (8.07 ± 2.63) | ─ | (7.89 ± 0.31) | ─ | ─ | (Ali et al., 2016) |
| Karnaphuli River, Chittagong (Winter) | ─ | ─ | (9.92 ± 2.78) | ─ | (8.17 ± 0.49) | ─ | ─ | (Ali et al., 2016) |
| Ground Water | ||||||||
| Mymensingh (Different types of Tubwells) | ─ | 4.636 | 1.123 | ─ | 7.077 | ─ | 369.615 | (Ahmed et al., 2010) |
| Cox's Bazar paleobeach area | ─ | ─ | 3.27 | 27 | 7.1 | 677 | ─ | (Seddique et al., 2016) |
| Rajshahi City (Shallow Tubwells) | ─ | ─ | ─ | (27.39 ± 0.68) | (6.91 ± 0.18) | (297.44 ± 49.7) | (445.44 ± 49.41) | (Mostafa et al., 2017) |
| Rajshahi City (Deep Tubwells) | ─ | ─ | ─ | (27.2 ± 0.54) | (7.0 ± 0.14) | (241.65 ± 21.7) | (454.98 ± 52.47) | (Mostafa et al., 2017) |
| Panchbibi, Joypurhat | ─ | ─ | ─ | ─ | (7.935 ± 0.46) | (270.48 ± 104.78) | (422.63 ± 163.73) | (Islam et al., 2017d) |
| Barguna (Shallow Tubewell) | ─ | ─ | ─ | 27.76 | 7.42 | 4829 | 8973 | (Islam et al., 2017d) |
| Bangladesh Standards (Drinking water) | 0.2 | 4.0 | 6.0 | 20–30 | - | 1000 | - | (DPHE, 2018) |
| Bangladesh Standard (Industrial Effluent) | 50 | 200 | 4.5–8.0 | 40–45 | 6–9 | 2100 | 1200 | (DoE, 2008) |
The temperature of the water should be 20–30 °C according to WHO standard. The temperature of water influences the aquatic life, solubility of solids, taste and odor, dissolved oxygen (DO), etc (Zuane, 1996). Although pH has no direct impact on the consumer, it is one of the most necessary operational water quality parameters (WHO, 2011). WHO recommended that the pH of the water be within 6.5–8.5. All studies found the pH of water sources within a suitable range. Total dissolved solids (TDS) constitute inorganic salts and small amounts of organic matter that are dissolved in water. TDS less than 600 mg/L is suitable for drinking water; but if the concentration level exceeds 1000 mg/L, the water becomes unpalatable (WHO, 2011). Some of the studies have found TDS level above the recommended limit. The conductivity of water can indicate the presence of minerals. Potable waters usually register conductivity from 50 to 500 micromhos/cm, but with mineralized water registering values over 500 (Zuane, 1996). No guideline value was proposed by WHO or Bangladesh Standard. A variety of conductivity value can be seen in different water sources based on various studies.
2.2. Major pollutants
2.2.1. Trace metals pollution
Trace element contamination of water is now a primary worldwide concern because even at low concentration these elements can show an adverse effect on living beings (Demira et al., 2015). Natural substances leached from the soil, run-off from agricultural activities, controlled discharge from sewage treatment works and industrial plants, and uncontrolled releases or leakage from landfill sites and chemical accidents or disasters are the sources of both surface and groundwater pollution (Leeuwen, 2000). Some of the trace elements are found to be essential for the human body (Bogden, 2000), but a negative impact on the living organism can be seen if the permissible limit is exceeded (Izah et al., 2016). In Bangladesh, trace elements in ground and surface water often exceed the guideline values recommended by WHO. Table 2 comprises the result of different studies on trace elements in water, which was conducted in the various area of Bangladesh in a different time.
Table 2.
Trace elements concentration (mg/L) in Bangladesh in surface water and groundwater. Data are extracted from various individual studies and arranged chronologically based on year of publication of the reviewed articles. Values given represent the mean values or mean values plus-minus standard deviation (S.D.), where the values with ± in the parenthesis () represents average ± S.D.
| Sampling Location | Cr | Cu | Fe | Mn | Ni | Zn | Cd | Pb | Reference |
|---|---|---|---|---|---|---|---|---|---|
| Surface Water | |||||||||
| Surma River (Monsoon Season) | 0.0376 | 0.0042 | 1.8340 | ─ | ─ | 0.0042 | ─ | 0.0130 | (Alam et al., 2007) |
| Surma River (Dry Season) | 0.0388 | 0.0042 | 0.3340 | ─ | ─ | 1.1540 | ─ | 0.0130 | (Alam et al., 2007) |
| Dhaleswari River | (0.4413 ± 0.0425) | (0.1547 ± 0.0305) | ─ | ─ | (0.0072 ± 0.0014) | ─ | (0.0065 ± 0.0009) | (0.0501 ± 0.0193) | (Ahmed et al., 2009) |
| Wetlands nearby Barapukuria, Dinajpur (Drainage Water) | <0.0720 | 0.2100 | 5.1000 | 0.1950 | 0.1800 | 0.4310 | ─ | 0.2300 | (Bhuiyan et al., 2010) |
| Wetlands nearby Barapukuria, Dinajpur (River Water) | 0.1000 | 3.1000 | 0.1630 | ─ | 0.5800 | ─ | 0.0700 | (Bhuiyan et al., 2010) | |
| Buriganga River, Dhaka | (0.587 ± 0.0441) | (0.1631 ± 0.0335) | ─ | ─ | (0.0088 ± 0.001) | ─ | (0.0093 ± 0.0015) | (0.0655 ± 0.0048) | (Ahmed et al., 2010) |
| Karatoa River | (0.005 ± 0.002) | Trace | (0.495 ± 0.247) | (0.101 ± 0.067) | (0.005 ± 0.003) | Trace | ─ | Trace | (Zakir et al., 2012) |
| Khiru River, Mymensingh | ─ | (0.0037 ± 0.001) | ─ | (0.0953 ± 0.110) | ─ | (0.0061 ± 0.003) | (0.1748 ± 0.340) | (0.0107 ± 0.008) | (Rashid et al., 2012) |
| Shitalakhya (2012) | 0.0050 | ─ | ─ | ─ | 0.0050 | 0.1060 | 0.0030 | 0.0050 | (Rahman et al., 2013) |
| Different Rivers near Dhaka | (0.0233 ± 0.0134) | (0.0147 ± 0.0148) | (0.0421 ± 0.0754) | (0.0312 ± 0.0399) | ─ | (0.002 ± 0.0017) | (0.0047 ± 0.0009) | (0.0041 ± 0.0008) | (Sikder et al., 2013) |
| Dhanmondi Lake, Dhaka | ─ | 0.0110 | ─ | 0.0528 | ─ | 0.0404 | 0.0097 | 0.0009 | (Mokaddes et al., 2013) |
| Romna Lake, Dhaka | ─ | 0.0110 | ─ | 0.0700 | ─ | 0.0379 | 0.0090 | 0.0013 | (Mokaddes et al., 2013) |
| Crescent Lake, Dhaka | ─ | 0.0110 | ─ | 0.0798 | ─ | 0.0189 | 0.0720 | 0.0009 | (Mokaddes et al., 2013) |
| Samshad Lake, Dhaka | ─ | 0.0168 | ─ | 0.0893 | ─ | 0.0238 | 0.0660 | 0.0007 | (Mokaddes et al., 2013) |
| Gulshan Lake, Dhaka | ─ | 0.0133 | ─ | 0.0904 | ─ | 0.0163 | 0.0277 | 0.0009 | (Mokaddes et al., 2013) |
| Bonani Lake, Dhaka | ─ | 0.0164 | ─ | 0.0896 | ─ | 0.0178 | 0.0102 | 0.0010 | (Mokaddes et al., 2013) |
| Sutrapur Lake, Dhaka | ─ | 0.0143 | ─ | 0.1020 | ─ | 0.6983 | 0.0834 | 0.0031 | (Mokaddes et al., 2013) |
| Rampura Lake, Dhaka | ─ | 0.0162 | ─ | 0.0916 | ─ | 0.6250 | 0.0044 | 0.0052 | (Mokaddes et al., 2013) |
| Airport Lake, Dhaka | ─ | 0.0129 | ─ | 0.1085 | ─ | 1.2801 | 0.2210 | 0.0007 | (Mokaddes et al., 2013) |
| Tongi Lake, Dhaka | ─ | 0.1150 | ─ | 0.0987 | ─ | 0.9980 | 0.0030 | 0.0014 | (Mokaddes et al., 2013) |
| Balu River (Winter Season) | (1.02 ± 0.24) | (0.16 ± 0.04) | (0.16 ± 0.02) | ─ | ─ | (0.38 ± 0.08) | ─ | ─ | (Hasan et al., 2014) |
| Balu River (Rainny Season) | ─ | (0.08 ± 0.04) | (0.04 ± 0.02) | ─ | ─ | (0.05 ± 0.02) | ─ | ─ | (Hasan et al., 2014) |
| Dhalai Beel and Bangshi River | (0.093 ± 0.032) | (1.05 ± 0.22) | ─ | (0.088 ± 0.017) | (0.035 ± 0.012) | (3.32 ± 0.62) | (0.007 ± 0.001) | (0.108 ± 0.031) | (Rahman et al., 2014)) |
| Paira River (Winter) | 0.0579 | 0.0351 | ─ | ─ | 0.0406 | ─ | 0.0009 | 0.0288 | (Islam et al., 2015a) |
| Paira Rive (Summer) | 0.0326 | 0.0240 | ─ | ─ | 0.0279 | ─ | 0.0005 | 0.0214 | (Islam et al., 2015a) |
| Korotoa River, Bogra (Summer) | (0.073 ± 0.027) | (0.061 ± 0.028) | ─ | ─ | (0.032 ± 0.019) | ─ | (0.008 ± 0.006) | (0.027 ± 0.015) | (Islam et al., 2015b) |
| Korotoa River, Bogra (Winter) | (0.083 ± 0.027) | (0.073 ± 0.033) | ─ | ─ | (0.039 ± 0.023) | ─ | (0.011 ± 0.008) | (0.035 ± 0.019) | (Islam et al., 2015b) |
| Buriganga River, Dhaka | 0.1140 | 0.2390 | 0.6120 | 0.1570 | 0.1500 | 0.3320 | ─ | 0.1190 | (Bhuiyan et al., 2015) |
| Karnaphuli River, Chittagong (Summer) | (0.0696 ± 0.0170) | ─ | ─ | ─ | ─ | ─ | (0.0065 ± 0.003) | (0.0099 ± 0.0048) | (Ali et al., 2016) |
| Karnaphuli River, Chittagong (Winter) | (0.0869 ± 0.0174) | ─ | ─ | ─ | ─ | ─ | (0.0106 ± 0.0045) | (0.0168 ± 0.0062) | (Ali et al., 2016) |
| Turag River | 0.0070 | Trace | ─ | ─ | ─ | 0.0900 | 0.0010 | 0.0090 | (Rabbi et al., 2016) |
| Ground Water | |||||||||
| Rajarampur, Chapai Nawabgonj | ─ | 0.0002 | ─ | ─ | <0.00006 | 0.03 | ─ | 0.0002 | (Islam et al., 2000) |
| Shamta, Jessore | <0.0002 | ─ | ─ | ─ | <0.00006 | 0.027 | ─ | 0.0005 | (Islam et al., 2000) |
| Mainamoti, Comilla | 0.0031 | 0.0006 | ─ | ─ | 0.001 | 0.053 | ─ | 0.001 | (Islam et al., 2000) |
| Andulia, Jhenidah | ─ | ─ | ─ | ─ | <0.00006 | 0.078 | ─ | 0.0007 | (Islam et al., 2000) |
| Supply groundwater of Banani | ─ | ─ | 0.04 | 0.02 | ─ | ─ | ─ | ─ | (Nahar et al., 2014) |
| Supply groundwater of Tejgaon | ─ | ─ | 0.11 | 0.05 | ─ | ─ | ─ | ─ | (Nahar et al., 2014) |
| Supply groundwater of Dhanmondi | ─ | ─ | 0.03 | 0.1 | ─ | ─ | ─ | ─ | (Nahar et al., 2014) |
| Supply groundwater of Hazaribagh | ─ | ─ | 0.02 | 0.09 | ─ | ─ | ─ | ─ | (Nahar et al., 2014) |
| Well water in Dhamrai | ─ | ─ | 15.9 | 0.86 | ─ | ─ | ─ | ─ | (Nahar et al., 2014) |
| Well water in Chuadanga | ─ | ─ | 28.9 | 0.29 | ─ | ─ | ─ | ─ | (Nahar et al., 2014) |
| Tube wells of Singair, Manikgonj | 0.093 | 0.0223 | 7.11 | 2.08 | 0.043 | 0.0643 | ─ | 0.019 | (Halim et al., 2014) |
| Pumping well of Faridpur | ─ | ─ | (5.9516 ± 4.9312) | (0.0006 ± 0.0007) | (0.0033 ± 0.0023) | (0.0104 ± 0.0102) | ─ | (0.0006 ± 0.0004) | (Bodrud-Doza et al., 2016) |
| Shallow Tubewells of Cox's Bazar paleobeach area | ─ | ─ | 1.81 | 1.87 | ─ | ─ | ─ | ─ | (Seddique et al., 2016) |
| Deep Tubewells of Cox's Bazar paleobeach area | ─ | ─ | 2.67 | 1.37 | ─ | ─ | ─ | ─ | (Seddique et al., 2016) |
| Different types of well in Lakshimpur | ─ | ─ | (3.235 ± 3.868) | (0.652 ± 0.583) | (0.0002 ± 0.0001) | ─ | ─ | (0.00004 ± 0.0001) | (Bhuiyan et al., 2016) |
| Deep Tubwell of Rajshahi City | ─ | (0.08 ± 0.06) | (3.1 ± 0.64) | (1.47 ± 0.78) | ─ | (0.19 ± 0.07) | (0.014 ± 0.01) | (1.167 ± 0.14) | (Mostafa et al., 2017) |
| Sylhet district | ─ | ─ | (6.832 ± 6.046) | (0.281 ± 0.217) | ─ | ─ | ─ | ─ | (Islam et al., 2017a) |
| Rangpur | ─ | ─ | (7.7264 ± 6.5593) | (0.6845 ± 0.7547) | ─ | (0.0333 ± 0.03899) | ─ | ─ | (Islam et al., 2017b) |
| WHO Standards | 0.05 | 2.00 | 0.30∗ | 0.5 | 0.02 | 3.00 | 0.003 | 0.01 | |
| Bangladesh Standards (Drinking water) | 0.05 | 1.00 | 0.30–1.00 | 0.1 | 0.10 | 5.00 | 0.005 | 0.05 | |
| Bangladesh Standards (Industrial effluents) | 0.50 | 0.50 | 2.00 | 5.00 | 1.00 | 5.00 | 0.05 | 0.10 | (DoE, 2008) |
Chromium (Cr) presents in nature chiefly in two oxidation states, Cr (III) and Cr (VI), which possess contrasting physiological effects (Aranda et al., 2010). According to WHO and Bangladesh standards, the maximum concentration of chromium in drinking water is 0.05 mg/L. BNDWQS report showed that 97.7% of the total samples contained less than 0.005 mg/L of Cr. Other individual studies reported that surface water in different location exceeds the maximum concentration value and it varied from 0.005 to 1.02 mg/L; whereas in groundwater, the values remain in between less than 0.0002–0.093 mg/L of Cr (Table 2). Balu river and Buriganga river shows a higher concentration of chromium. Ahmed et al. (2011b) found that the average concentration of chromium is 0.587 mg/L in river Buriganga. A study conducted by Hasan et al. (2014) in Balu river showed that the concentration of chromium is in between 0.62 to 1.37 mg/L in the dry season, but absent in rainy season. A selected few studies focused on the chromium content in groundwater. The highest chromium concentration (0.093 mg/L) in groundwater was found in Singair Upazila, Manikgonj (Halim et al., 2014). Overall, surface water contains significantly more chromium than that of groundwater. Chromium in its Cr(VI) oxidation state, is responsible for lung cancer, nasal irritation, nasal ulcer, hypersensitivity reactions, and contact dermatitis when it entered into human bodies via dermal and inhalation routes (Shrivastava et al., 2002).
Copper (Cu) is an indispensable trace element which shows a significant role in the biochemistry of all living organisms (Bremner and Beattie, 1990). WHO prescribed the maximum acceptable concentration of 2 mg/L for Cu. BNDWQS (2009) report suggested that 100% of the samples had less amount of Cu than the WHO and Bangladesh standards. Various studies calculated the Cu content in both surface and groundwater throughout the country, but concentration never exceeded the maximum limit. The highest mean concentration of Cu in surface water (0.239 mg/L) and groundwater (0.08 mg/L) was reported from Buriganga river (Bhuiyan et al., 2015) and Rajshahi city (Mostafa et al., 2017), respectively. Excess copper accumulation leads to copper toxicosis which results in hepatic cirrhosis, hemolytic anemia, and degeneration of the basal ganglia (Harris and Gitlin, 1996).
Iron (Fe) is one of the most abundant trace elements found in earth's crust, but iron deficiency is a global concern (Quintero-Gutiérrez et al., 2008). It was calculated that only 60% of water samples were below the Bangladesh standard (1.0–0.3 mg/L) in BNDWQS (2009) report. This survey also indicated the high average concentration of Fe present in the shallow (2.65 mg/L) and deep tubewell (1.37 mg/L) water throughout the country. Various individual studies also showed the exceeding present of iron in water of Bangladesh. High degree of Fe contamination in surface water has been reported in the rivers near Barapukuria coal mine, Dinajpur due to anthropogenic inputs (3.1 mg/L) (Bhuiyan et al., 2010), followed by Surman river during monsoon (1.834 mg/L) (Alam et al., 2007). Groundwater Fe contamination is even more severe; the concentration range varies from 0.02 to 28.9 mg/L. The maximum average Fe concentration (28.9 mg/L) was determined in the arsenical well water of Chuadanga (Nahar et al., 2014). Table 2 shows that groundwater of different districts from different parts of Bangladesh is severely contaminated with Fe. Overdosing of iron is potentially hazardous and plays a vital role in causing diabetes (Swaminathan et al., 2007), anemia and hemochromatosis (Toyokuni, 2009), lung and heart disease (Milman et al., 2001).
Manganese (Mn) has been reported to be exigent in every animal species studied (Goldhaber, 2003). In Bangladesh, none of the studies indicated any Mn contamination is surface water (Table 2); however, the existence of Mn above the WHO standard limit (0.5 mg/L) was reported in ground water throughout the country. The highest mean concentration of Mn in groundwater was found in the water sample of the tubewell water in Singair, Manikgonj (Halim et al., 2014). An elevated level of Mn was found in shallow tubewell (1.87 mg/L) in Cox's Bazar area; the deep water sample collected from the same area also showed a significant presence of Mn due to high rock-groundwater interaction (Seddique et al., 2016). A study conducted in Greece reported that individuals who consumed drinking water containing more than 1.8 mg/L Mn, exhibited neurologic symptoms which are similar to Parkinson's disease (Kondakis et al., 1989). Hallucinations, memory impairment, disorientation, and emotional instability also caused by Mn overdose (Gupta and Gupta, 1998).
Nickel (Ni) is a nutritionally essential trace element for humans as well as other animal species and plants. But Ni can affect the mass population through contaminated drinking water and food intake (Cempel and Nikel, 2005). According to WHO standards, Ni concentration should not exceed 0.02 mg/L in drinking water; whereas Bangladesh standard allows the presence of Ni up to 0.1 mg/L in drinking water and 1 mg/L for industrial discharge. Studies suggested the average concentration ranges between 0.005-0.18 mg/L and >0.00006–0.043 mg/L in surface water and groundwater, respectively. The maximum average concentration (0.18 mg/L) of this trace element was found in the wetlands near Barapukuria coal mine, Dinajpur (Bhuiyan et al., 2010). Nickel hypersensitivity also responsible for asthma, conjunctivitis, inflammatory reactions to nickel-containing prostheses and implants (Nielsen et al., 1999). Moreover, Nickel compounds can cause cancer (Bal et al., 2000).
Zinc (Zn) is a natural trace element found in all plants and animals which maintaining the healthy growth of the human body, especially for infants and young children's growth and development (Askary et al., 2011). Bangladesh standard and WHO permissible limit of Zn for drinking water is 5 mg/L and 3 mg/L respectively for drinking water. The highest level of Zn was found in the Dhalai Beel and Bangshi River which was slightly above (3.32 mg/L) the WHO limit. Ingestion of acute zinc can cause vomiting, diarrhea, neurological damage ("Zn shakes") (Gupta and Gupta, 1998) and chronic exposure to Zinc is responsible for depressed Cu utilization (Sandstead, 1978), Fe deficiency, lowered levels of HDL cholesterol (Hooper, 1980).
Cadmium (Cd) is considered as a very toxic trace metal because of its extremely long half-life (Jihen et al., 2008). According to WHO standards, its concentration should not exceed 0.003 mg/L in drinking water. But, in Bangladesh separate investigation showed a significant amount of Cd present throughout the country in different forms of surface water (Table 2). Although there are almost no data about the condition of Cd contamination in groundwater, a recent study reported the mean concentration of Cd almost five times higher (0.014 mg/L) than the WHO limit in the tubewell water in Rajshahi city (Mostafa et al., 2017). The maximum concentration of Cd (0.221 mg/L) was reported in the Airport lake of Dhaka city (Mokaddes et al., 2013).
Lead (Pb) is a ubiquitous trace metal and significant public health concern, particularly in developing countries (Flora et al., 2012). The highest admissible concentration set by WHO and Bangladesh standard for Pb in drinking water is 0.01 mg/L and 0.05 mg/L respectively. In some region of Bangladesh, water sources contain a much higher amount of Pb than WHO permissible limit. The ranges of Pb concentration varied between 0.00 to 0.23 mg/L for surface water and 0.00004–1.167 mg/L for groundwater. Bhuiyan et al. (2010) evaluated trace metals in the wetlands near Barapukuria, Dinajpur and indicated exceed the amount of Pb (0.23 mg/L) in the analyzed samples. Rivers like Buriganga (Bhuiyan et al., 2015), Korotoa (Islam et al., 2015b), Paira (Islam et al., 2015a), Khiru (Rashid et al., 2012), Bangshi (Rahman et al., 2014) showed elevated amount of Pb. In groundwater, however, the maximum mean concentration of Pb was more than hundred times (1.167 mg/L) that of WHO limit which was found in deep tubewell water of Rajshahi city (Mostafa et al., 2017).
2.2.1.1. Arsenic pollution
Arsenic is a fatal element (Lindsay and Maathuis, 2017) which is named as a category 1 carcinogenic element by WHO (Driscoll et al., 2004). The first survey done in Bangladesh to identify arsenic was in late 1990s (Ravenscroft, 2011). In 1999, groundwater from 64 districts of Bangladesh was analyzed where 52 districts contained arsenic levels greater than 0.01 mg/L, and 42 districts where the level was greater than 0.042 mg/L (Uttam and Chowdhury, 2000). The allowable concentration of arsenic for drinking water indicated by WHO is 0.01 mg/L where 0.05 mg/L is permitted in Bangladesh but studies found that 8.4% tube-wells in Bangladesh contain more than 0.3 mg/L arsenic (Smith et al., 2000).
Several local and foreign organization examined the level of arsenic contamination in Bangladesh. Among them, BBS/UNICEF (2011) found that 8% of samples they tested, surpassed the Bangladesh standard value and 18% samples surpassed the WHO guideline value according to their research center information. According to the Digital Arsenator data, they also found that 13.4% and 32% samples surpassed the Bangladesh standard value and WHO guideline value respectively. Similarly, another survey collected samples throughout the whole nation and found that 12.6% of samples surpassed the Bangladesh standard value (BBS/UNICEF, 2010).
In Bangladesh, groundwater from “tableland” territory contains more arsenic than “flood plain” and “delta” area. Deposition of Holocene sediments may be the possible reasons behind this difference (Chakraborti et al., 2015). Pond water also is not free from high level of arsenic (Yokota et al., 2001). Arsenic contamination level in different cities/districts of Bangladesh is summarized in Table 3.
Table 3.
Arsenic contamination in various cities/districts of Bangladesh. All values are given in μg/L. Source: (Chakraborti et al., 2010)
| Division | City/district name | Total no. of samples | Distribution of total samples in different as concentration (μg/L) ranges |
Maximum concentration detected (μg/L) | |||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
| <10 | 10 to 50 | 51 to 99 | 100 to 299 | 300 to 499 | 500 to 699 | 700 to 1000 | >1000 | ||||
| Dhaka | Dhaka | 574 | 449 | 29 | 26 | 63 | 7 | - | - | - | 352 |
| Faridpur | 707 | 243 | 171 | 67 | 142 | 40 | 24 | 12 | 8 | 1630 | |
| Gazipur | 3386 | 3312 | 33 | 8 | 16 | 16 | 1 | - | - | 533 | |
| Gopalgonj | 384 | 86 | 74 | 55 | 146 | 19 | 2 | 2 | - | 920 | |
| Jamalpur | 144 | 89 | 30 | 7 | 6 | 2 | 2 | 6 | 2 | 1172 | |
| Madaripur | 2309 | 453 | 480 | 336 | 622 | 316 | 76 | 21 | 5 | 1200 | |
| Kishoreganj | 1328 | 527 | 429 | 238 | 133 | 1 | - | - | - | 365 | |
| Manikganj | 282 | 79 | 101 | 44 | 55 | 2 | 1 | - | - | 586 | |
| Munshiganj | 151 | 10 | 6 | 12 | 80 | 36 | 7 | - | - | 529 | |
| Mymensingh | 1825 | 1705 | 101 | 12 | 6 | 1 | - | - | - | 330 | |
| Narayanganj | 412 | 54 | 42 | 34 | 147 | 68 | 36 | 26 | 5 | 1750 | |
| Narshingdi | 336 | 252 | 16 | 7 | 23 | 24 | 10 | 4 | - | 1000 | |
| Netrokona | 533 | 201 | 180 | 84 | 49 | 13 | 6 | - | - | 580 | |
| Rajbari | 174 | 79 | 72 | 5 | 15 | 1 | - | 2 | - | 714 | |
| Shariatpur | 152 | 63 | 29 | 20 | 26 | 12 | 2 | - | - | 580 | |
| Sherpur | 303 | 191 | 100 | 7 | 5 | - | - | - | - | 275 | |
| Tangail | 597 | 443 | 131 | 21 | 2 | - | - | - | - | 224 | |
| Chittagong | Bandarban | 41 | 41 | - | - | - | - | - | - | - | - |
| Brahmanbaria | 47 | 12 | 9 | 9 | 17 | - | - | - | - | 210 | |
| Chandpur | 1165 | 50 | 36 | 30 | 675 | 294 | 54 | 21 | 5 | 1318 | |
| Chittagong | 366 | 319 | 26 | 13 | 8 | - | - | - | - | 275 | |
| Comilla | 545 | 113 | 26 | 29 | 128 | 123 | 75 | 25 | 26 | 1769 | |
| Cox's Bazar | 58 | 58 | - | - | - | - | - | - | - | - | |
| Feni | 186 | 58 | 53 | 40 | 28 | 5 | 1 | 1 | - | 1000 | |
| Khagrachari | 39 | 39 | - | - | - | - | - | - | - | - | |
| Lakshmipur | 2262 | 304 | 235 | 339 | 852 | 421 | 246 | 177 | 88 | 2030 | |
| Noakhali | 843 | 5 | 36 | 92 | 413 | 80 | 79 | 48 | 90 | 4730 | |
| Rangamati | 47 | 47 | - | - | - | - | - | - | - | - | |
| Rajshahi | Bogra | 767 | 607 | 125 | 17 | 16 | 1 | - | - | 1 | 1040 |
| Dinajpur | 2641 | 2612 | 28 | 1 | - | - | - | - | - | 77 | |
| Gaibanda | 1233 | 863 | 308 | 40 | 17 | 4 | 1 | - | - | 512 | |
| Joypurhat | 398 | 388 | 10 | - | - | - | - | - | - | 32 | |
| Kurigram | 539 | 467 | 72 | - | - | - | - | - | - | 50 | |
| Lalmanirhat | 464 | 434 | 30 | - | - | - | - | - | - | 50 | |
| Naogaon | 537 | 527 | 10 | - | - | - | - | - | - | 22 | |
| Natore | 117 | 91 | 22 | 4 | - | - | - | - | - | 63 | |
| Nawabganj | 1902 | 920 | 434 | 173 | 273 | 57 | 23 | 12 | 10 | 1600 | |
| Nilphamari | 523 | 505 | 18 | - | - | - | - | - | - | 50 | |
| Pabna | 5117 | 1595 | 1807 | 807 | 691 | 124 | 52 | 25 | 16 | 2108 | |
| Panchagarh | 462 | 458 | 4 | - | - | - | - | - | - | 15 | |
| Rajshahi | 2698 | 2197 | 266 | 105 | 121 | 8 | 1 | - | - | 524 | |
| Rangpur | 464 | 285 | 114 | 19 | 20 | 15 | 9 | 2 | - | 939 | |
| Sirajganj | 278 | 187 | 79 | 8 | 4 | - | - | - | - | 216 | |
| Thakurgaon | 461 | 416 | 38 | 6 | 1 | - | - | - | - | 130 | |
| Khulna | Bagherhat | 371 | 90 | 72 | 34 | 79 | 67 | 17 | 12 | - | 958 |
| Chuadanga | 457 | 124 | 223 | 73 | 11 | 11 | 13 | 2 | - | 841 | |
| Jessore | 5465 | 4227 | 248 | 317 | 457 | 105 | 76 | 32 | 3 | 1120 | |
| Jhenaidaha | 388 | 185 | 142 | 24 | 27 | 6 | 4 | - | - | 592 | |
| Khulna | 1000 | 518 | 233 | 55 | 138 | 39 | 6 | 5 | 6 | 3143 | |
| Kusthia | 2065 | 1082 | 557 | 154 | 168 | 42 | 33 | 13 | 16 | 2190 | |
| Meherpur | 1024 | 526 | 271 | 95 | 95 | 27 | 5 | 4 | 1 | 1230 | |
| Magura | 496 | 243 | 168 | 44 | 33 | 5 | - | - | 3 | 1050 | |
| Narail | 371 | 96 | 56 | 35 | 164 | 20 | - | - | - | 375 | |
| Satkhira | 532 | 32 | 73 | 56 | 236 | 133 | 1 | 1 | - | 750 | |
| Barisal | Barguna | 43 | 35 | 8 | - | - | - | - | - | - | 15 |
| Barisal | 803 | 179 | 113 | 40 | 227 | 106 | 75 | 47 | 16 | 1770 | |
| Bhola | 74 | 57 | 17 | - | - | - | - | - | - | 50 | |
| Jhalakati | 42 | 17 | 16 | 3 | 5 | 1 | - | - | - | 310 | |
| Patuakhali | 15 | 13 | 2 | - | - | - | - | - | - | 10 | |
| Pirojpur | 124 | 42 | 41 | 8 | 24 | 8 | - | 1 | - | 731 | |
| Sylhet | Habiganj | 103 | 59 | 37 | 6 | 1 | - | - | - | - | 100 |
| Moulavi Bazar | 152 | 72 | 65 | 12 | 3 | - | - | - | - | 133 | |
| Sunamganj | 89 | 6 | 34 | 29 | 17 | 3 | - | - | - | 302 | |
| Sylhet | 391 | 331 | 44 | 14 | 2 | - | - | - | - | 177 | |
| Total | 52202 | 29768 | 8230 | 3714 | 6487 | 2263 | 938 | 501 | 301 | - | |
| Percentage (%) | 57 | 15.8 | 7.1 | 12.4 | 4.3 | 1.8 | 1 | 0.6 | |||
In short, arsenic pollution is a genuine risk to drinking water in Bangladesh, overexposure of arsenic not only increases the probability of diseases like lung cancer, renal cancer, skin cancer but also it may create a generation like “arsenic orphans” (Flanagan et al., 2012).
2.2.2. Major cations and anions
Water of surface and ground sources contain several cations and anions; among those, cations like sodium (Na+), potassium (K+), calcium (Ca2+), magnesium (Mg2+), ammonium (NH4+) and anions like chloride (Cl−), fluoride (F−), nitrates (NO3-), bicarbonate (HCO3-), sulfates (SO42-), phosphates (PO43-) etc. are found to be essential for humans. Nevertheless, an excess amount of these ions can make the water unsuitable for humans as well as other living organisms. Table 4 represents the summarized data of the condition of different ions in various water sources, which are extracted from numerous studies throughout the country.
Table 4.
Cation and anion concentration (mg/L) in Bangladesh in surface water and groundwater. Data are extracted from various individual studies and arranged chronologically based on year of publication of the reviewed articles. Values given represents the mean values or mean values plus-minus standard deviation (S.D.), where the values with ± in the parenthesis () represents average ± S.D.
| Samples Location | Na+ | K+ | Ca2+ | Mg2+ | NH4+ | Cl- | F- | NO3- | HCO3-/CO2- | SO42- | PO42- | References |
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Surface Water | ||||||||||||
| Surma River (Dry) | ─ | ─ | ─ | ─ | (0.18 ± 0.09) | ─ | ─ | ─ | ─ | ─ | ─ | (Alam et al., 2007) |
| Surma River (Monsoon) | ─ | ─ | ─ | ─ | (0.12 ± 0.07) | ─ | ─ | ─ | ─ | ─ | ─ | (Alam et al., 2007) |
| Mouri River | 25.968 | 3.68 | 69.717 | 48.33 | ─ | ─ | ─ | 1.277 | ─ | 49.507 | 7.765 | (Kamal et al., 2007) |
| Sadar ghat, Buriganga River (Rainny Season) | ─ | ─ | ─ | ─ | ─ | ─ | ─ | Trace | ─ | ─ | ─ | (Saha et al., 2009) |
| Sadar ghat, Buriganga River (Winter Season) | ─ | ─ | ─ | ─ | ─ | ─ | ─ | Trace | ─ | ─ | ─ | (Saha et al., 2009) |
| Surface Water near Dhaka-Narayanganj-Demra (D.N.D) Embankment | ─ | ─ | ─ | ─ | ─ | (3699.83 ± 2136.28) | (3.33 ± 3.53) | (55.80 ± 66.81) | ─ | (1443.87 ± 1962.82) | (292.89 ± 66.68) | (Sultana et al., 2009) |
| Barapukuria, Dinajpur (Drainage Water) | ─ | 7.37 | 26.2 | ─ | ─ | ─ | ─ | ─ | ─ | ─ | ─ | (Bhuiyan et al., 2010) |
| Barapukuria, Dinajpur (Ground Water) | ─ | 2.13 | 7.11 | ─ | ─ | ─ | ─ | ─ | ─ | ─ | ─ | (Bhuiyan et al., 2010) |
| Buriganga River, Dhaka (Different Seasons) | 252.78 | 40.25 | 27.547 | ─ | ─ | 68.74 | ─ | 1.715 | ─ | ─ | 2.13 | (Ahmed et al., 2011b) |
| Katrnatoli River, Savar, Dhaka (Different Seasons) | 113.43 | 7.11 | 20.37 | ─ | ─ | 26.407 | ─ | 1.333 | ─ | ─ | 3.803 | (Ahmed et al., 2011b) |
| Ashulia, Dhaka | ─ | ─ | ─ | ─ | ─ | (81.67 ± 21.38) | ─ | (7.42 ± 3.35) | ─ | (94.42 ± 33.71) | (4.62 ± 1.24) | (Bhuiyan et al., 2011) |
| Amin Bazar, Dhaka | ─ | ─ | ─ | ─ | ─ | (93 ± 38.01) | ─ | (7.61 ± 3.64) | ─ | (78.75 ± 30.82) | (5.38 ± 1.28) | (Bhuiyan et al., 2011) |
| Tejgaon area, Dhaka (Wet Season) | ─ | ─ | ─ | ─ | ─ | ─ | ─ | 6.7 | ─ | ─ | ─ | (Mondol et al., 2011) |
| Tejgaon area, Dhaka (Dry Season) | ─ | ─ | ─ | ─ | ─ | ─ | ─ | 198.3 | ─ | ─ | ─ | (Mondol et al., 2011) |
| Karatoa river | (15.94 ± 2.88) | (15.03 ± 2.34) | (44.32 ± 9.04) | (15.84 ± 5.53) | ─ | (3.12 ± 0.66) | ─ | ─ | (2.59 ± 1.12) | (7.43 ± 5.19) | (1.58 ± 0.37) | (Zakir et al., 2012) |
| Turag river | ─ | ─ | ─ | ─ | ─ | 34 | ─ | ─ | ─ | ─ | ─ | (Banu et al., 2013) |
| Shitalakshyaa River | ─ | ─ | ─ | ─ | ─ | 67.5 | ─ | 1 | ─ | ─ | 0.825 | (Sikder et al., 2013) |
| Turagh River | ─ | ─ | ─ | ─ | ─ | 7.5 | ─ | 1.5 | ─ | ─ | 1.75 | (Sikder et al., 2013) |
| Bongshi River | ─ | ─ | ─ | ─ | ─ | 10 | ─ | 2 | ─ | ─ | 0.983 | (Sikder et al., 2013) |
| Karnaphuli River, Chittagong (Summer) | ─ | ─ | ─ | ─ | (0.193 ± 0.09) | ─ | ─ | ─ | ─ | ─ | ─ | (Ali et al., 2016) |
| Karnaphuli River, Chittagong (Winter) | ─ | ─ | ─ | ─ | (0.3 ± 0.11) | ─ | ─ | ─ | ─ | ─ | ─ | (Ali et al., 2016) |
| Ground Water | ||||||||||||
| Chandpur | 347.4417 | 7.624 | 64.733 | 45.488 | 9.48 | 602.213 | ─ | 0.553 | 286.917 | 20.268 | 4.547 | (Zahid et al., 2008) |
| Sirajdikhan, Munshiganj | (64.751 ± 73.634) | (10.106 ± 5.224) | (87.493 ± 41.445) | (44.336 ± 24.636) | ─ | (69.027 ± 96.983) | ─ | (3.930 ± 6.931) | (478.231 ± 181.080) | (5.230 ± 2.312) | (1.761 ± 1.603) | (Halim et al., 2009) |
| Bagerhat (Deep Tubewell) | 437.5 | 6.15 | 16.77 | 18.19 | ─ | 167.67 | ─ | 5.87 | 270.44 | 6.43 | ─ | (IWM, 2009) |
| Sonargaon, Narayanganj | 22.743 | 3.578 | 67.992 | 16 | 1.049 | 35.458 | ─ | 0.0822 | 272.55 | 1.542 | 3.55 | (Bhattacharya et al., 2009) |
| Chandina, Comilla | 123.456 | 9.52 | 24.267 | 33.7 | 9.288 | 153.878 | ─ | 0.104 | 307.111 | 0.5289 | 8.1578 | (Bhattacharya et al., 2009) |
| Mymensingh (Different types of Tubwells) | ─ | ─ | 37.917 | ─ | 0.963 | ─ | ─ | ─ | ─ | ─ | 0.823 | (Ahmed et al., 2010) |
| Ishwardi Municipal Area, Pabna (Dry Season) | 26.129 | 7.014 | 65.031 | 41.531 | ─ | 74.656 | ─ | 1.421 | 386.861 | 2.952 | 5.856 | (Hossain et al., 2010) |
| Ishwardi Municipal Area, Pabna (Wet Season) | 31.051 | 7.344 | 70.230 | 45.780 | ─ | 70.451 | ─ | 1.760 | 398.818 | 2.813 | 6.270 | (Hossain et al., 2010) |
| Eastern region of Bangladesh | (90.41 ± 206.67) | (9.14 ± 12.53) | (36.75 ± 23.19) | (23.88 ± 21.78) | ─ | (135.36 ± 311.96) | ─ | (9.1 ± 12.54) | (166.84 ± 123.27) | (11.26 ± 31.73) | (3.24 ± 1.69) | (Halim et al., 2010) |
| Noakhali (Shallow Tubewell) | ─ | ─ | ─ | ─ | ─ | 875.61 | ─ | 3.91 | 305.12 | 4.39 | ─ | (Ahmed et al., 2011a) |
| Satkhira (Deep Tubewell) | 221.96 | 13.4 | 62.8 | 14.13 | ─ | 409.6 | ─ | 12.05 | 224.32 | 11.79 | ─ | (Rahman et al., 2011) |
| Mirpur, Dhaka city | 15.1 | 2.1 | 14.6 | 0.41 | ─ | 12.9 | ─ | 8.9 | 66 | 0.3 | ─ | (Nahar et al., 2014) |
| Banani, Dhaka city | 16.8 | 1.7 | 27.3 | 6.69 | ─ | 13 | ─ | 3.8 | 81 | 0.7 | ─ | (Nahar et al., 2014) |
| Tejgaon, Dhaka city | 24.3 | 2 | 27.7 | 9.02 | ─ | 56.7 | ─ | 20.5 | 86 | 19.5 | ─ | (Nahar et al., 2014) |
| Dhanmondi, Dhaka city | 32 | 1.9 | 54.4 | 1.69 | ─ | 50.1 | ─ | 9.7 | 174 | 15.5 | ─ | (Nahar et al., 2014) |
| Hazaribagh, Dhaka city | 43.5 | 1.9 | 45 | 16.9 | ─ | 46.8 | ─ | 0.03 | 179 | 31.6 | ─ | (Nahar et al., 2014) |
| Motijhil, Dhaka city | 21.9 | 2 | 29.6 | 11.9 | ─ | 25.4 | ─ | 10.1 | 122 | 14.6 | ─ | (Nahar et al., 2014) |
| Armanitola, Dhaka city | 27.6 | 2.4 | 49.5 | 19.3 | ─ | 41.2 | ─ | 0.03 | 222 | 7.2 | ─ | (Nahar et al., 2014) |
| Savar, Dhaka | 7.5 | 2 | 6.4 | 1.54 | ─ | 2.8 | ─ | 9 | 27 | 0.1 | ─ | (Nahar et al., 2014) |
| Dhamrai, Dhaka | 25.2 | 3 | 78.1 | 24.3 | ─ | 40.9 | ─ | 0.3 | 399 | 16.8 | ─ | (Nahar et al., 2014) |
| Chuadanga (Arsenates well water) | 117.9 | 9.5 | 294 | 70.9 | ─ | 632 | ─ | 0.03 | 700.2 | 0.1 | ─ | (Nahar et al., 2014) |
| Singair, Manikgonj | 27.3 | 8.8 | 72.3 | 36.4 | 0.5 | 38.1 | ─ | 1.4 | 179 | 17.7 | 2.6 | (Halim et al., 2014) |
| Faridpur | 13.598 | 8.788 | 120.032 | 28.22 | ─ | 17.288 | ─ | 2.371 | 616.359 | 6.20725 | ─ | (Bodrud-Doza et al., 2016) |
| Gupalganj (Deep Tubewell) | 180.77 | 3.47 | 53.08 | 22.81 | ─ | 96.52 | ─ | ─ | ─ | 39.35 | 0.93 | (Shammi et al., 2016) |
| Lakshmipur (Deep Tubewell) | 159.78 | 10.89 | 55.76 | 46.14 | ─ | 227.2 | ─ | ─ | 430.18 | 16.14 | ─ | (Bhuiyan et al., 2016) |
| Rajshahi City (Shallow Tubwells) | (23.12 ± 1.96) | (5.66 ± 0.57) | (78.35 ± 7.6) | (27.02 ± 2.13) | ─ | (55.315 ± 9.9) | ─ | (1.60 ± 0.48) | (245.30 ± 29.59) | (38.76 ± 5.2) | ─ | (Mostafa et al., 2017) |
| Rajshahi City (Deep Tubwells) | (22.77 ± 2.24) | (5.63 ± 0.52) | (78.54 ± 0.38) | (26.22 ± 1.66) | ─ | (44.9 ± 9.7) | ─ | (1.67 ± 0.51) | (188.36 ± 2.28) | (36.6 ± 2.92) | ─ | (Mostafa et al., 2017) |
| Sylhet | (47.167 ± 30.962) | (2.396 ± 1.782) | (7.183 ± 6.354) | (4.156 ± 3.083) | ─ | (12.331 ± 15.738) | ─ | (3.188 ± 7.320) | (147.659 ± 72.066) | (2.952 ± 5.214) | ─ | (Islam et al., 2017a) |
| Panchbibi, Joypurhat | (12.168 ± 2.102) | (0.301 ± 0.094) | (54.708 ± 4.385) | (4.036 ± 1.276) | ─ | ─ | (0.052 ± 0.022) | ─ | (136.971 ± 20.336) | (1.513 ± 0.242) | ─ | (Islam et al., 2017c) |
| Khulna (Shallow Tubewell) | 647.2 | 17.05 | 101.5 | 78.28 | ─ | 1776.74 | ─ | 2.61 | 510.05 | 4.97 | ─ | (Islam et al., 2017e) |
| Patuakhali (Deep Tubewell) | 78.99 | 3.8 | 12.47 | 9.34 | ─ | 298.13 | ─ | 11.57 | 391.02 | 12.5 | ─ | (Islam et al., 2017f) |
| Barguna (Shallow Tubewell) | 863 | 16.16 | 136 | 155 | ─ | 3513 | ─ | 4.12 | 254 | 19.48 | ─ | (Islam et al., 2017d) |
| WHO Standards | 200 | ─ | 100 | 150 | ─ | 250 | ─ | 50 | ─ | 500 | ─ | (WHO, 2011) |
| Bangladesh Standards (Drinking water) | 200 | 12 | 75 | 30–35 | 0.2 | 150–600 | 1 | 10 | ─ | 400 | 6 | (DPHE, 2018) |
| Bangladesh Standards (Industrial effluent) | ─ | ─ | ─ | ─ | ─ | 600 | 7–15 | ─ | ─ | ─ | ─ | (DoE, 2008) |
2.2.2.1. Cations
Sodium (Na+) is very common is drinking water and mostly found as NaHCO3 and Na2SO4 (Whelton et al., 2007). WHO and Bangladesh standard for the maximum Na+ concentration is 200 mg/L. A few studies found Na+ limit above the standard in many water sources; mostly in groundwater sources. In case of surface water, the highest mean concentration of Na+ (252.78 mg/L) throughout the different season was found in Buriganga river (Ahmed et al., 2011b). Although most of the studies reported a mild concentration of Na+ in selected groundwater, water in some territory showed a higher amount of Na+. The maximum level of Na+ (863 mg/L) in groundwater was reported in the shallow tube well of Barguna district (Islam et al., 2017d). Sodium is one of the leading constituents of the blood plasma of humans and because of that reason alteration of its normal concentration in the human body may have direct and vital effects on the osmotic pressure of the plasma, on plasma and interstitial fluid volumes, on acid-base balance, on the maintenance of the electrical activity of body cells, and on the responsiveness of the cardiovascular system to circulating endogenous pressor agents (Grollman, 1961).
The amount of potassium (K+) found in water is less than other major cations, and it is mostly present in water as KHCO3, K2SO4 and KCl (Whelton et al., 2007). 93% of the tested sample collected from all over the country reported in BNDWQS (2009) result did not surpass the Bangladesh standard value for K+. This particular report also indicated that Jhaloka, Noakhali, Chuadanga, and Meherpur were the four districts, which exhibited a higher concentration of K+ than the standard value in drinking water. Individual investigations also agreed with the BNDWQS report on K+ contamination in Bangladesh. Same as Na+, Buriganga river water contained the highest amount of K+, which is more than thrice that of standard value (40.25 mg/L) (Ahmed et al., 2011b). Apart from the water of the Karatoa river, most of the surface water sources contained an insignificant amount of K+ (Table 4). Shallow tube well water in Khulna showed the highest concentration of K+ (17.05 mg/L) found in groundwater sources (Islam et al., 2017e). Potassium enters into the human body mostly through the intake of different solid foods, and this metal helps to decrease blood pressure and also reduces cardiovascular disease. But high potassium intake may result in Hyperkalaemia, which eventually can lead to cardiac arrhythmias (He and MacGregor, 2008).
Calcium (Ca2+) is the amplest mineral in the human body, and this metal plays a vital role in cellular activities, hormones, cancer, heart disease, and muscle and neurodegenerative diseases, as well as the descent of the testis (Tandouan and Ulusu, 2005). None of the studies found Ca2+ above the safe limit in surface water; however, some of the groundwater sources showed an excess amount of Ca2+. 294 mg/L of Ca2+ was found in the water of arsenates well of Chuadanga district (Nahar et al., 2014). Individual studies and BNDWQS report showed the similar condition of Ca2+ in the water of districts like Rajshahi, Faridpur, Dhaka, Munshiganj, which are above the recommended limit. The significant side effects from excessive consumption of calcium are hypercalcemia, hypercalciuria, urinary tract calculi, calcification in a variety of soft tissues, notably in the kidney and in arterial walls, and suppression of bone remodeling (Heaney et al., 1982).
Magnesium (Mg2+) is a vital nutrient for human as well as other animals, and it is the second most abundant mineral in the human body (Vallee et al., 1960). Higher concentration of Mg2+ in any source of water is uncommon in Bangladesh. Studies suggested that water of Khulna and Chittagong territory possessed a higher amount of Mg2+ in both surface and groundwater (Table 4). Although very little data can be found regarding the Mg2+ in surface water, one study conducted in the river Mouri situated in Khulna, reported the excess amount of Mg2+ (48.33 mg/L) in that stream (Kamal et al., 2007). In addition, investigation in the water of shallow tubewell of Khulna showed 78.28 mg/L mean concentration of Mg2+ (Islam et al., 2017e). But the highest average concentration of Mg2+ (155 mg/L), which is almost five times that of standard value; was found in the shallow tube well of Barguna district which is also situated in Khulna division (Islam et al., 2017d).
The non-ionized ammonia (NH3) and ionized ammonium (NH4+) in the environment originate from metabolic, agricultural and industrial processes, and from disinfection with chloramine (WHO, 2011). There is no specific guideline value for NH4+ set by WHO. A few studies calculated the amount of NH4+ present in the water of Bangladesh. According to the studies, the highest concentration (9.48 mg/L) of ammonium was found in the groundwater of Chandpur (Zahid et al., 2008). Ammonia does not directly affect health, but it can compromise the disinfection efficiency of water (WHO, 2011).
2.2.2.2. Anions
Chloride (Cl−) is a naturally occurring anion, which can be found in every water sources, and it is a relatively minor contaminant (Kelly et al., 2012). In case of Cl−, there is no guideline value provided by WHO, whereas Bangladesh standard for Cl− ranges between 150-500 mg/L for drinking water and 600 mg/L for industrial effluent discharge. Different studies on water sources revealed the amount of Cl− in water. The highest mean concentrations of Cl− have been reported from surface water near D.N.D (Dhaka- Narayanganj-Demra) embankment which was 3699.83 mg/L; more than six times higher than the standard industrial discharge limit because of the high discharge rate of the textile dyeing effluents (Sultana et al., 2009). In case of groundwater, the highest amount of Cl− (1776.74 mg/L) was recorded from the shallow tube well in Khulna area (Islam et al., 2017e). Different studies also found an elevated amount of Cl− in the groundwater sample of Noakhali (Ahmed et al., 2011a) and Chandpur (Zahid et al., 2008). Chloride is present in water can increase the rate of metal corrosion in the distribution pipeline. Also, the excess amount of chloride can change the natural odor and taste of water (WHO, 2011).
Fluoride (F−) is often found in minerals, and it can be leached out due to erosion by rainwater, which leads to contamination of ground and surface waters; also, industrial effluents contribute increasing the amount of F− (Sun et al., 2011). The average concentration of the F- present in the water according to BNSWQS (2009) report is only 0.20 mg/L. Only two individual studies investigated F− content in surface and groundwater respectively. An article on the highly polluted surface water of D.N.D embankment found 3.33 mg/L mean concentration of fluoride (Sultana et al., 2009).
Nitrate (NO3-) is a naturally occurring ion, which is concerned with the nitrogen cycle (Fewtrell, 2004). Contamination of drinking water supplies with NO3- and nitrite (NO2-) is one of the three major water-quality problems today, ranking with contamination of water with bacteria and toxic chemicals (Johnson and Kross, 1990). WHO guideline value for NO3- and NO2- is 50 mg/L and 3 mg/L respectively whereas Bangladesh standard for this ion is maximum of 10 mg/L. Tejgaon is one of the major industrial areas of Dhaka city which is severely polluted. One study was undertaken in this area showed a very high average concentration of NO3- in the nearby lagoon, which was 198.3 mg/L (Mondol et al., 2011). Another study conducted in another industrial area near Dhaka found NO3- concentration just above the safe limit in surface water (Sultana et al., 2009). None of the studies found and groundwater containing NO3- above the WHO standard, but several areas exceeded Bangladesh standard. Bacterial conversion of the relatively innocuous nitrate ion to nitrite can lead to the development of Methemoglobinemia, which can be the cause of infant death (Winton et al., 1971). Many types of research have shown the relation between consumption of high nitrate containing drinking water and the incidence of different cancers.
Bicarbonate (HCO3-) is a simple single carbon molecule that plays surprisingly vital roles in diverse biological processes (Casey, 2006). HCO3- is associated with the hardness of water; hardness of water is usually expressed as milligrams of calcium carbonate per liter (WHO, 2011). There is no particular guideline value for bicarbonate ion. Different studies found the bicarbonate content in groundwater varied from 27 mg/L to 700.2 mg/L (Table 4). Sulfate (SO42-) is another naturally occurring mineral, which can be found in surface and groundwater. There is no definite guideline value set by WHO for SO42-, but more than 500 mg/L of sulfate in drinking water is not recommended (WHO, 2011). In Bangladesh, both surface and groundwater sources showed an insignificant amount of SO42- present in water. The only surface water of D.N.D embankment areas exhibited a very high concentration of SO42-, which was 1443.87 mg/L (Sultana et al., 2009). Higher concentration of sulfate present in drinking water can cause a mild laxative effect manifested by slightly looser and heavier stools and may lead to disease like diarrhea (Heizer et al., 1997). Phosphate (PO43-) in water bodies can cause eutrophication, hence the amount of PO43- should be low (Zhang et al., 2011). WHO hasn't established any guideline value for this particular ion. Only one investigation found overplus amount of PO43- (292.89 mg/L) in the surface water near D.N.D embankment (Sultana et al., 2009).
2.2.3. Bacteriological contamination
Microbial examination of water is typically occurred to identify mostly fecal coliforms (Azizullah et al., 2011). Generally, fecal coliforms found in the dung of different warm-blooded species like human, domestic animals (Geldreich, 1996). Scientist uses it as an indicator of water pollution as the presence of waterborne human disease-causing bacteria is indicated by this coliform (Shiekh, 2006). WHO standard for fecal and total coliforms for drinking water is 0 coliform per 100mL of water samples (WHO, 2004). A considerable lot of the revealed types of bacteria can cause serious medical issues in Table 5. Numerous examinations uncover overwhelming bacteriological contamination of drinking water in the country which is summarized in Table 6.
Table 5.
List of bacteria reported in drinking water in Bangladesh and their possible health effects.
| Bacteria | Possible health effects | References |
|---|---|---|
| Aeromonas hydrophila | Variety of diseases like septicemia, gastroenteritis in young children and elderly | (Ahmed, 2013) |
| Enterobacter aerogenes | Cause infections in urinary and respiratory tracts | (De Gheldre, 1997) |
| Enterococcus species | Cause infection in urinary tract | (Felmingham, 1992) |
| Escherichia coli | Cause food poisoning, gastroenteritis, urinary tract infections | (Todar, 2007) |
| Klebsiella species | An astute pathogen that ordinarily causes nosocomial contaminations in the urinary tract, respiratory tract, lung, wound destinations | (Chung, 2016) |
| Listeria species | Variety of diseases like meningitis, endocarditis and has high mortality rate | (Acharjee, 2011; Sauders et al., 2012) |
| Pseudomonas aeruginosa | Causes diseases in newborns and elderly patients | (Ahmed, 2013) |
| Salmonella species | Typhoid | (Farooqui, 2009) |
| Shigella species | Cause abdominal pain, tenesmus, watery diarrhea | (Baron, 1996) |
| Staphylococcus species | Cause superficial skin lesions, food poisoning | (Baron, 1996) |
| Vibrio cholerae | Cholera | (Herrington, 1988; Alam, 2006) |
Table 6.
Bacteriological contamination of drinking water in different areas of Bangladesh. Data are collected from various studies done in Bangladesh.
| Sampling Location | No. of Samples | Total Coliforms Counts/100mL | Fecal Coliforms Counts/100 mL | References |
|---|---|---|---|---|
| Tube-well water, Matlab, Chandpur | 5 | 5 | 3 | (Islam et al., 2001) |
| Buriganga River | 6 | – | 5.25×105 | (Shiekh, 2006) |
| Turag River | 6 | – | 6.08×104 | (Shiekh, 2006) |
| Balu River | 6 | – | 4.08×104 | (Shiekh, 2006) |
| Dhanmondi Lake, Dhaka | 6 | – | 2.55×104 | (Shiekh, 2006) |
| Gulshan Lake, Dhaka | 6 | – | 2.39×105 | (Shiekh, 2006) |
| Nobab-bari Pond, Dhaka | 6 | – | 5.77×105 | (Shiekh, 2006) |
| Jatrabari Pond, Dhaka | 6 | – | 5.57×105 | (Shiekh, 2006) |
| Airport Road Pond, Dhaka | 6 | – | 3.57×103 | (Shiekh, 2006) |
| Curzon Hall Pond, Dhaka | 6 | – | 2.65×104 | (Shiekh, 2006) |
| Sher-E-Bangla Agriculture University Pond, Dhaka | 6 | – | 2.16×103 | (Shiekh, 2006) |
| Institute of Public Health Pond, Dhaka | 6 | – | 5.53×105 | (Shiekh, 2006) |
| River Water, Dhaka City | 18 | 2.4×104 | 2.4×104 | (Parveen, Microbial Contamination of Water in Around Dhaka City, 2008) |
| Pond Water, Dhaka City | 18 | 2.4×104 | 2.4×104 | (Parveen, Microbial Contamination of Water in Around Dhaka City, 2008) |
| Tube-well water, Dhaka city | 19 | 1.0×101 | 0 | (Parveen, Microbial Contamination of Water in Around Dhaka City, 2008) |
| Household Water of Dhaka city | 45 | 1.7×0102 | 1.7×0102 | (Parveen, Microbial Contamination of Water in Around Dhaka City, 2008) |
| Mineral Water, Dhaka City | 9 | 0 | 0 | (Parveen, Microbial Contamination of Water in Around Dhaka City, 2008) |
| Different locations of Chittagong city | 14 | 2.01×102 | 1.4×101 | (Zuthi, 2009) |
| Tube-well water, Gakulnagar, Savar, Dhaka | 20 | 3 | – | (Rahman, 2009) |
| Tubewell Water in Dhaka City | 19 | 1.0×101 | – | (Islam, 2010) |
| Mineral Water in Dhaka City | 8 | 1.7×101 | – | (Islam, 2010) |
| Filtered Water in Dhaka City | 8 | 2.90×102 | – | (Islam, 2010) |
| Municipal Tap Water in Dhaka City | 10 | 6.32×102 | – | (Islam, 2010) |
| Different locations of Dhaka city | 18 | 1 | 1 | (Acharjee, 2011) |
| Samples from RWHSs (dry season) | 20 | – | 4.65×102 | (Islam, 2011) |
| Samples from RWHSs (wet season) | 23 | – | 1.5×103 | (Islam, 2011) |
| Samples from CRWHSs (dry season) | 14 | – | 1.7×102 | (Islam, 2011) |
| Samples from CRWHSs (wet season) | 14 | – | 8.56×102 | (Islam, 2011) |
| Samples from PSFs (dry season) | 17 | – | 2.99×102 | (Islam, 2011) |
| Samples from PSFs (wet season) | 14 | – | 4.14×102 | (Islam, 2011) |
| Ponds (dry season) | 39 | – | 2.01×103 | (Islam, 2011) |
| Ponds (wet season) | 39 | – | 4.44×103 | (Islam, 2011) |
| WASA supplied water, Dhaka city | 20 | 5.53×102 | 2.60×102 | (Sabrina, 2013) |
| Tube-well water, Sinduria, Dhaka | 21 | 8.44×103 | 5.16×102 | (Rahman, 2013) |
Most of the rural people in Bangladesh use tube-well water for drinking purposes, but this tube-well water is contaminated by micro-organisms (Islam et al., 2001). In Gakulnagar village in the Dhaka district, 60% of tube-well water is contaminated by coliform bacteria (Rahman, 2009). Moreover, another study found three tube-wells are highly contaminated with total coliforms in Sardarkandi village under Dhaka district (Ferguson et al., 2011). Similarly, from Comilla, Brahmanbaria and Sirajganj districts 207 samples of tube-well water were collected, and among them, 41% samples were polluted by total coliforms, also 29% samples by thermos-tolerant coliforms and 13% samples by Escherichia coli (Luby et al., 2008). Another study collected samples from 21 shallow tube-wells from Shinduria village under Savar sub-district of Dhaka district and found total coliforms ranging from 1.5×101 to 4.98 × 104 cfu/100mL and fecal coliforms 0 to 3.49 × 103 cfu/100mL (Rahman, 2013). A recent study collected 53 tube-well water samples from different districts of the country and found that 81.2% of them were contaminated with coliforms (Parvez, 2016).
In Bangladesh, pond water also is not free from fecal coliforms and other pathogenic bacteria (Albert, 2000; Alam, 2006). A study collected 120 samples from 5 ponds around Dhaka city, and among the five, four ponds were highly polluted by fecal coliforms ranging from 1.63×104 to 6.48 × 105 cfu/100mL (Islam, 1994). Similarly, a recent study tested 12 pond water samples across the country and found all of the ponds were contaminated with coliforms (Parvez, 2016). People from coastal areas of Bangladesh drink pond water in the dry season (Frisbie, 2002) and the alarming fact is those pond waters contain fecal coliforms. In coastal regions of Dacope and Mongla sub-district of the Khulna and Bagerhat districts, a study collected 39 samples of pond water and found fecal coliforms ranging from 12 to 104 cfu/100mL (Islam, 2011).
Though one study found no bacterial contamination in the WASA treated water (Acharjee, 2011), several other studies found bacterial contamination not only in the WASA treated water but also in other government and non-government water treating agency including in the bottled mineral water. A study found high numbers of pathogenic bacteria both in the WASA supply points and in the consumer points. They found high amount of Salmonella spp., Shigella spp., Aeromonas spp., Vibrio spp., Listeria spp., Pseudomonas spp. and Staphylococcus spp. bacteria's in those supply points (Acharjee et al., 2014). Similarly, another study tested ten municipal tap water samples, eight filtered water samples, eight mineral water samples and found total coliform ranging from 150 to 1100 cfu/100mL in the municipal tap water, 63 to 1100 cfu/100mL in the filtered water and 2 to 47 cfu/100mL in the mineral water samples. They also found Escherichia coli (60%), Klebsiella (40%), Enterobacter (20%), Pseudomonas (70%), Proteus (10%), Staphylococcus (40%) and Salmonella (0%) in the municipal tap water samples (Islam, 2010). Moreover, another study found that the water supplied by WASA in Dhaka city is highly contaminated with fecal coliforms such as fecal coliforms found in Basabo (2.8×103 c.f.u/100mL), in Sobujbag (5.2×106 c.f.u/100mL), in Shagun Bagichaa and Mohammadpur (5.0×103 c.f.u/100mL) (Sabrina, 2013). In Chittagong city, water supplied by CWASA was also contaminated by fecal coliforms (Zuthi, 2009). Similarly, another study reported that 75% of water samples collected from tube-wells of Rajshahi city is polluted by total coliforms, of which 59% polluted by fecal coliforms (Rasul, 2010).
Escherichia coli is also a detector of fecal contamination (Ferguson, 2012; Talukdar, 2013). A study collected samples from rural shallow tube-wells of the country and found that Escherichia coli concentrations were within ranges of 1–10, 10–100 and 100–2000 MPN/100mL on 30%, 9%, 4% samples respectively (van Geen et al., 2011). In Dhaka city, out of 175 tap water samples 80% of their water samples were contaminated with fecal coliforms, 38% samples had fecal coliforms more than 104 cfu/100 mL, and also 63% of total water samples contained E. coli (Talukdar, 2013). In Mymenshing district, among the tube-well water samples, in 14% of the samples, E. coli were average ten cfu/100mL, and in 3% of the samples, E. coli were 100cfu/100mL (Ercumen, 2015).
There are several causes for contamination of drinking water. Groundwater might be polluted by various kinds of human activities. Residential, metropolitan, business activities would all be able to affect groundwater quality. Contamination of tube well water seems identified with various components, including nearness of toilets or channels to the tube wells, depth of the tube-wells. Distribution pipes might pollute supplied water because of spillage (Parvez, 2016).
2.2.4. Pesticides
Pesticides are lethal to living beings which are used for controlling plant bugs (Chowdhury et al., 2013). In 1951, pesticide was first used in Bangladesh for treating pest during cultivation and for improving production (Rahman, 1997). The use of pesticide in Bangladesh is increasing day by day (Matin et al., 1998). Rahman et al. (1995) reported that the consumption of pesticide in Bangladesh was double within six years. Moreover, Rahman (1997) reported that in 1956–57, around 2 tons of pesticide imported in Bangladesh and the consumption of pesticide increased per year such a high rate that eight metric ton pesticide was imported in Bangladesh in 1993. A few data is available regarding pesticide pollution of drinking water in Bangladesh. Lack of funds and laboratory facilities are the main obstacles in the availability of data in the country. The results of different examinations detailing pesticide deposits in ground and surface water of Bangladesh are abridged in Table 7, and WHO standards for different pesticide residues are in Table 8.
Table 7.
Pesticide concentrations (ppm) in surface and groundwater sample of Bangladesh. Data are extracted from different studies and values given represent the mean values or the range from minimum to maximum.
| Sampling Location | Water Type | Pesticide detected | Concentration | Reference |
|---|---|---|---|---|
| BIT, Khulna | Surface Water | DDT | 0.0195 | (Rahman, 1997) |
| DDE | 0 | |||
| Endrin | 0 | |||
| Heptachlor | 0.0002 | |||
| Kittonkhola, Barisal | Surface water | DDT | 0.035 | (Rahman, 1997) |
| DDE | 0 | |||
| Endrin | 0 | |||
| Heptachlor | 0.0002 | |||
| Anowara, Chittagong | Surface water | DDT | 0 | (Rahman, 1997) |
| DDE | 0 | |||
| Endrin | 0.075 | |||
| Heptachlor | 0 | |||
| Amin Bazar, Dhaka | Surface water | DDT | 0 | (Rahman, 1997) |
| DDE | 0.01 | |||
| Endrin | 0.014 | |||
| Heptachlor | 0.00023 | |||
| Baman Danga Beel | Surface water | p,p'-DDE | 0 | (Rahman, 1997) |
| Dieldrin | 0.00064 | |||
| p,p'-DDT | 0.0015 | |||
| Hand Tubewel (Nayerhat, Dhaka) | Groundwater | p,p'-DDE | 0 | (Rahman, 1997) |
| Dieldrin | Traces | |||
| p,p'-DDT | Traces | |||
| Niger bell (Comilla) | Surface water | p,p'-DDE | 0.0001 | (Rahman, 1997) |
| Dieldrin | 0 | |||
| p,p'-DDT | 6×10−6 | |||
| Begumgonj, Sylhet | Surface water | p,p'-DDE | 0.00046 | (Rahman, 1997) |
| Dieldrin | 0 | |||
| p,p'-DDT | 0.019 | |||
| Water samples collected from different regions of Bangladesh | Surface water | p,p'-DDE | 0.013–0.060 | (Matin et al., 1998) |
| p,p'-DDD | 0.014–0.038 | |||
| p,p'-DDT | 0.015–0.068 | |||
| Heptachlor | 0.150–1.020 | |||
| samples collected from different regions of Bangladesh | Groundwater | p,p'-DDE | 0.010–0.084 | (Matin et al., 1998) |
| p,p'-DDD | 0.014–0.365 | |||
| p,p'-DDT | 0.027–1.204 | |||
| Heptachlor | 0.025–0.789 | |||
| Samples collected at 48 different locations in Bangladesh | Surface water | Aldrin | ND | (Islam, 2007) |
| Dieldrin | ND | |||
| Endrin | ND | |||
| p,p'-DDT | ND-0.5401 | |||
| Heptachlor | ND-1.479 | |||
| Lindane | ND-1.826 | |||
| Pond Water samples collected from different regions of Bangladesh | Surface water | Aldrin | ND | (Bagchi, 2009) |
| Dieldrin | ND | |||
| Endrin | ND | |||
| DDT | ND-0.316 | |||
| DDD | ND-0.052 | |||
| DDE | ND-0.014 | |||
| Lindane | ND | |||
| Heptachlor | ND-0.048 | |||
| Carbaryl | ND-0.609 | |||
| Carbofuran | ND-1.760 | |||
| Pond water collected from Nabinagar Upazila under Brahmanbaria district | Surface water | Malathion | ND-0.0463 | (Uddin, 2012) |
| Carbofuran | ND-0.0629 | |||
| Cypermethrin | ND-0.09 | |||
| Samples collected from Savar and Dhamrai Upazila | Surface water | Malathion | ND-105.2 | (Chowdhury, 2012) |
| Diazinon | ND-0.9 | |||
| Carbaryl | ND-18.1 | |||
| Carbofuran | ND-198.7 | |||
| Samples collected from the paddy fields, Rangpur district | Surface water | Chlorpyrifos | ND-1.189 | (Chowdhury et al., 2012) |
| Carbofuran | ND-3.395 | |||
| Carbaryl | ND-0.163 | |||
| Samples collected from pond water in Meherpur zilla | Surface water | Diazinon | ND-0.0775 | (Uddin, 2012) |
| Chlorpyriphos | ND-0.0143 | |||
| Carbofuran | ND-0.0387 | |||
| Carbaryl | ND | |||
| Water samples collected from Jessore region | Surface water | Quinaphos | ND-0.241 | (Fatema, 2013) |
| Water samples from the lakes, Rangpur district | Surface water | Chlorpyrifos | 0.544–0.895 | (Chowdhury et al., 2012) |
| Carbofuran | 0.949–1.671 | |||
| Carbaryl | ND-0.195 | |||
| Samples collected from different spots in Bangladesh | Surface water | Aldrin | ND | (Chowdhury et al., 2013) |
| Dieldrin | ND | |||
| DDE | ND-4.06 | |||
| DDD | ND | |||
| DDT | ND-8.29 | |||
| Endrin | ND | |||
| Lindane | ND | |||
| Heptachlor | ND-5.24 | |||
| Water samples collected from near the vegetable fields of Savar Upazila | Surface water | DDT | BDL | (Hossain et al., 2015) |
| Chlorpyrifos | BDL-9.31 | |||
| Diazinon | BDL-7.86 | |||
| Ethion | BDL | |||
| Fenthion | BDL-56.3 | |||
| Fenitrothion | BDL-33.41 | |||
| Malathion | BDL-59.9 | |||
| Parathion | BDL-6.23 | |||
| Carbaryls | BDL-6.3 | |||
| Carbofuran | BDL-43.2 | |||
| Cypermethrin | BDL-80.5 | |||
| Methoxychlor | BDL | |||
| Samples collected at different spots from Dhamrai Upazila | Both surface and groundwater | Malathion | ND-922.8 | (Hasanuzzaman et al., 2016) |
| Diazinon | ND-31.5 |
ND, not detected; BDL, below detection Limit.
Table 8.
WHO standards of pesticide residues for drinking water quality (WHO, 2008).
| Quality Parameter | WHO Standard (in ppm) |
|---|---|
| 2,4-DDD | 0.001 |
| 2,4-DDT | 0.001 |
| 4,4-DDT | 0.001 |
| Aldrin | 0.00003 |
| Carbofuran | 0.007 |
| Dieldrin | 0.00003 |
| Dimenthoate | 0.006 |
| Endosulfane | 0.00025 |
| Endrin | 0.0006 |
| Lindane | 0.002 |
| Chlorpyrifos | 0.03 |
| Heptachlor | 0.00003 |
Rice, wheat, jute, potato, sugarcane, vegetables, and tea are the main crops cultivated in the country (Chowdhury et al., 2013). The paddy fields consume 70% of the total pesticides (Bhattacharjee, 2013). In Bangladesh, insecticides are largely used than herbicides, fungicides, acaricides, and rodenticides. Miah (2014) also found that 20 types of insecticides, 18 types of fungicides and two types of rodenticides are applied in Bangladesh. Similarly, Rahman et al. (1995) reported that 95% of total pesticides, used in Bangladesh, are insecticides and the remaining 5% are fungicides, weedicides, and rodenticides. They also reported that among the pesticides, 60.4% are organophosphorus, 28.6% are carbamates, 7.6% are organochlorines and 3.4% are other compounds. Another study found that in Bnagladesh, carbamates are used in 64% of the area used for crop production and organophosphates are used in 35% of that area (Chowdhury et al., 2012).
After applying pesticide, rain runoff, the residues to the nearest water bodies and they become contaminated (Kreuger, 1998). (Islam, 2007) collected 48 agricultural field water samples from different regions in the country and found water samples from 10 locations were polluted by P, P-DDT, heptachlor, and lindane. P, P-DDT was found at Rajbari and Bogra districts, heptacholor was found at Dhaka, Magura, and Chittagong districts, lindane was found at Dhaka, Sylhet, Shariatpur and Noakhali districts, also the highest concentration of P, P-DDT residue was found Bogura, and it was 0.5401 ppm. In Savar and Dhamrai Upazila, out of 27 water samples, Diazinon and carbofuran were found in water samples from Savar Upazila at 0.9 ppm and 198.7 ppm, respectively. Malathion was found from Dhamrai Upazila at 105.2ppm. Carbaryl was also found ranging from 14.1 ppm to 18.1 ppm and carbofuran at 105.2 ppm in the Dhamrai Upazila (Chowdhury, 2012). In Savar Upazila, out of 12 water samples beside the agricultural fields, carbaryl residues were found ranging from 4.6 ppm to 6.3 ppm, carbofuran residues at 43.2 ppm, cypermethrin in three water samples ranged from 54.36 ppm to 80.5 ppm (Hossain et al., 2015). Similarly, Chowdhury et al. (2012) collected 16 water samples from paddy fields and lakes in Rangpur city and found chlopyrifos ranging from 0.554 ppm to 0.895 ppm, carbofuran ranging from 0.949 ppm to 1.671 ppm and carbaryl in one sample at 0.195 ppm in the lake water samples. In the paddy field water samples, they found, cholrpyrifos in seven samples ranging from 0.477 ppm to 1.189 ppm, carbofuran in seven samples ranging from 0.934 ppm to 3.395 ppm and carbaryl in two samples at 0.055 ppm and 0.163 ppm. Moreover, Chowdhury et al. (2013) collected irrigated water samples from 22 districts in Bangladesh. They found DDT residue in Feni, Rajshahi and Nawabganj districts. The highest DDT concentration was 8.29 ppm. They also found heptachlor residues in Natore, Sunamganj, and Madaripur districts and the highest concentration was 5.24 ppm. They also found both DDT and heptachlor residues in water samples from Chhatak at Sunamganj district.
Pond water can be contaminated by the pesticides used in crops field situated around the pond (Chowdhury et al., 2013). Several studies found pesticide residues in pond water samples. Bagchi (2009) collected 20 pond water samples and found DDE and heptachlor in one water sample and DDT, DDE, DDD in another sample but their concentration level was within the WHO guideline value of the water quality. They also found carbofuran residues in 10 water samples but that also within the WHO guideline value. Similarly, another study collected 25 pond water samples from Nabinagar Upazila (Brahmanbaria district) and found Malathaion in three samples ranging from 0.0241 ppm to 0.0463 ppm and that also within the WHO guideline value of water quality (Uddin, 2012). Another study done in the Rangpur district collected seven pond water samples, but they found no water samples contaminated with pesticide residues (Chowdhury et al., 2012). In Meherpur district, out of 20 pond water samples, diazoin was found in three samples ranging from 0.0328 ppm to 0.0790 ppm, and chlorpyriphos was found in two samples ranging from 0.0107 ppm to 0.0143 ppm (Uddin, 2013). In Dhamrai Upazila, Hasanuzzaman et al. (2016) collected six pond water samples for the analysis of Malathion residue and found Malathion residue ranging from 261.06 ppm to 922.8 ppm.
Groundwater levels in Bangladesh are high, and soil is mainly coarse, so there is a chance that groundwater can have polluted by pesticide residues. Matin et al. (1998) collected 144 groundwater samples from underground sources and found most of the samples were free from pesticide residues. All DDT values they found were ranging from 0.051 ppm to 1.653 ppm that were below the WHO recommended values. Also, they found heptachlor residues ranging from 0.025 ppm to 0.789 ppm.
Over the years it has been seen that the consumption and use of pesticide in the agricultural sector have increased and this is expected to continue for the next decades due to socio-economic and technological progress (Bempah, 2011). Most farmers in Bangladesh use pesticides excessively and purposelessly as they have little consciousness and knowledge about the use (Miah, 2014). Overuse of pesticides can cause genuine public health insecurity particularly as residues in food (Chowdhury, 2013). Several studies found pesticide residues in different vegetable samples like in tomato, Lady's finger, eggplant, long yard bean (Fatema, 2013; Miah, 2014; Rahman, 2015). Pesticide residues were also detected in meat, milk and dry fish samples (Rahman, 1997; BHUIYAN, 2009; Shoeb, 2016).
Most farmers used mainly organochlorine, organophosphorous and carbamate pesticides in Bangladesh (Dasgupta, 2007). Organochlorine pesticides like DDT, lindane, heptachlor, dieldrin were used in agricultural fields and to treat diseases like malaria in Bangladesh from the early fifties (Rahman, 2000). Organochlorine (DDT) was banned in 1993 in Bangladesh but there were reports that it is consumed illegally (Shoeb, 2016). Several studies found residues of DDT and its metabolites in fresh fish, dry fish and poultry feeds (Nahar, 2008; Shoeb, 2009). All the pesticides have negative effects on human. Organochlorine pesticide residues having low polarity, low aqueous solubility, high lipophilicity and a very stable half-life in the environment make it a potential threat to human health and environment as it can bioaccumulation in the food chain (El-Mekkawi, 2009; Afful, 2010). As organophosphorous pesticides are cheap and their effectiveness is very good, farmers are encouraged to use it. But these pesticides are harmful to farmer's health, and those pesticides are also genotoxic and carcinogenic (Chowdhury, 2012; Hayat, 2010). Chlorpyrifos can cause attention deficit hyperactivity disorder and development disorder both in fetuses and children (Rauh, 2006). Carbamate pesticides such as carbofuran cause major problems in the reproductive system (Goad, 2004) and carbaryl can cause nausea, vomiting, blurred vision and breathing difficulties (Kamrin, 1997).
2.3. Sources of water pollution
Water can be polluted by both natural and anthropogenic sources (Harrison, 2001). Majority of the water sources, chiefly surface water bodies, however, are polluted because of the industrial growth; urbanization and man-made problems (Pandey, 2006) (see Table 9). In Bangladesh, sewage and solid waste & industrial waste & effluents are the main cause of surface water pollution. Arsenic contamination in groundwater is devastating in case of Bangladesh, and an estimated 35 to 77 million people of this particular country have been chronically exposed to arsenic in their drinking water (Flanagan et al., 2012).
Table 9.
Point and non-point sources of water pollution in Bangladesh.
| Types of Pollutants | Point Sources | Non-point Sources |
|---|---|---|
| Pathogens | Raw sewage | Runoff from agricultural waste and chemicals |
| Urban solid waste | Septic tank leachate, Animal waste | |
| Excrement of human and animal | ||
| Heavy Metal | Discharge of industrial effluent | Pesticide runoff |
| Effluent from mines | Smelting | |
| Thermal power plants | ||
| Hospital and Pharmaceutical waste | ||
| Organic Chemical | Industrial effluent mostly from paper mills | Fertilizer, Pesticide, and Herbicide runoff |
| Urban solid and liquid waste | Runoff from pasture and farms, household | |
| Nutrients | Wastewater from treatment plants | Runoff agricultural waste and chemicals |
| Thermal | Electric Power Plants | |
| Industrial effluents | ||
| Sedimentation | Runoff from construction sites less than 20,000 m2 | Runoff from construction sites more than 20,000 m2 |
| Agricultural runoff | ||
| Radioactivity∗ | Discharge from nuclear plants | Natural occurring radioactivity |
Country's first 2.4 GWe nuclear power plant –Rooppur Nuclear Power Plant—is under construction. Adopted from (Cunningham and Cunningham, 2011; Botkin and Keller, 2011; Miller and Spoolman, 2016).
Industrial pollutants are the major cause of surface water pollution in the urban region in Bangladesh. According to an industrial survey conducted by Bangladesh Center for Advanced Studies (BCAS) in 2009, only about 40% of industries had ETPs. In 10% of industries, ETPs were under construction at that time, and about 50% of industries have no ETP establishment (Amin, 2015). In terms of overall emission (indicated as BOD and TSS) into water, pulp and paper industry is the major contributor (47%), followed by pharmaceuticals (16%), metal (14%) and food industries (12%), fertilizers/pesticides (7%), industrial chemicals (1%) and other industries (3%) which includes the cumulative contribution of cement and clay, textile, wood and furniture, tanneries and leather and petroleum industries (Rasul et al., 2006). Dhaka and it's adjacent districts like Gazipur, Narayanganj are the worst victim of unplanned industrialization; hence, exhibit drastic pollution in water sources. Although Dhaka City is surrounded by some peripheral rivers, the water of these rivers is too contaminated to use as potable water. There are 19 primary and at least 41 secondary discharge points to the rivers within the city (IWM, 2007). Improper discharge of untreated wastewater from various industries neighboring these rivers adulterates the water quality (Rahman and Hossain, 2008; Subramanian, 2004; Karn and Harada, 2001; Kamal et al., 1999). A World Bank study reported that peripheral rivers of Dhaka took 1.5 million cubic meters of wastewater every day from 7,000 industrial units in surrounding areas and another 0.5 million cubic meters from other sources (Islam, 2010a). Before relocating to Savar Upazila, Dhaka (Roy, 2017), tanneries located in Hazaribagh and Rayer Bazar in Dhaka city were responsible for discharging 15,000 cubic meters of liquid wastes, 19,000 kilograms of solid wastes and 17,600 kilograms of BOD into Buriganga river daily (Rahman and Bakri, 2010). Kaliakoir Upazila of Gazipur is only 25 km northeast of the capital city where an unplanned industrial cluster has been developed in the past 20 years. These industries are discharging 30 billion liters of effluent water annually in the nearby waterbodies such as Mokosh Beel, Turag river and Ratanpur Khal (Chowdhury and Clemett, 2006). Large numbers of textile dyeing industries along with other industries situated surrounding D.N.D embankment discharge a large amount of effluents and solid wastes into different waterbodies which eventually enter into the Shitalakshya River. Almost 80% of the total industries does not have any treatment plant and hence discharge toxic untreated industrial effluent into those waterbodies (Sultana et al., 2009).
A vast amount of untreated effluents from industries such as spinning mills, dying, cotton, textile, steel mills, oil refineries, and others industries is discharged regularly into the Karnaphuli river, Chittagong (Ali et al., 2016). Ship Breaking industry is one of the fastest growing industries in Bangladesh which is a significant contributor of trace metal pollution in seawater and groundwater in the coastal region of Bangladesh (Hasan et al., 2013).
Pollution of closed water bodies caused by human waste is a major problem in Bangladesh (Chowdhury, 2010). According to previous statistics, it is estimated that 16,380 tons of waste were produced in Bangladesh every day (Sujauddin et al., 2008). Urban cities are the worst victim of this kind of water pollution. The wastewater discharge from Dhaka city dwellers is about 1.22 million m3/day, whereas the only sewage treatment plant in Dhaka, namely “Pagla Sewage Treatment Plant” can treat 0.12 million m3 wastewater per day (Akter et al., 2017). The surface water quality in the two river systems and other surface water bodies, e.g. khals (small waterbody) and ponds in Dhaka have very high BOD, COD, and E-coli content which indicates discharge of untreated industrial effluents and domestic sewage. Moreover, only 50% of the municipal solid waste being collected by the two city corporations of Dhaka results in most of the wastes dumped into water bodies, low lying areas and khals (Anonymous, 2010). Among the total habitat of Dhaka, 15% use pit latrines and 30% use open latrines; the sewage generated from these latrines are mostly released without any treatment into low-lying areas and river water (Alam, 2009).
The agriculture sector is the economic backbone of Bangladesh which represents 15.33% of the Gross Domestic Product (GDP) and contributes almost half of the country's economic output (Uddin, 2013). Different types of organophosphorus and carbamate pesticides are used extensively by the local farmers, but due to the lack of proper knowledge and instruction, they overuse these pesticides (Chowdhury, 2012; Bhattacharjee et al., 2012). Haphazard use of pesticides leads to both surface and groundwater pollution, chiefly caused by rain or runoff water from the agricultural land (Hasanuzzaman et al., 2016). A World Bank survey reported that 6% of the total pesticides applied to crops are extremely hazardous (Meisner, 2004). Nitrate, phosphate, potassium, aldrin, dieldrin, chlardane, indrin, cadmium, arsenic, chromium and other toxins extracted from different kinds of agrochemical eventually get mixed with the water of various waterbodies (Rahman and Debnath, 2015). Furthermore, pesticide leaching into groundwater can contaminate the water (Anwar and Saing, 2010).
Arsenic contamination in groundwater is a major threat to public health in Bangladesh (Smith et al., 2000). Groundwater pollution is very alarming for Bangladesh as 95% of drinking water is derived from groundwater sources (Chowdhury, 2010). Although the sources of higher concentration of arsenic present in the groundwater in Bangladesh is ambiguous, different theories have been developed (Islam et al., 2000; Das et al., 2004). Initially, various anthropogenic sources such as pesticides, industrial waste, tubewell filters, etc. were considered as the leading sources of arsenic in groundwater, but field observations reported that the source of this trace metal was in geological deposits (Fazal et al., 2001). Even though there is three arsenic ore in the world, Fazal et al. (2001) stated that Arsenopyrite or ferrous arsenic sulfide (FeAsS) is the main source of arsenic pollution in Bangladesh. Pyrite Oxidation and Oxy-hydroxide Reduction are the two hypotheses developed to explain the mobilization of arsenic.
Other minor sources also contribute to the contamination of water bodies. Bhuiyan et al. (2010) showed that Barapukuria coal mine is responsible for heavy metal and thermal pollution in nearby water systems. Accidental oil spill also can cause severe damage to the water quality and aquatic life forms of large water bodies. A recent ‘oil spill from a crashed tanker’ incident resulted in an estimated 350,000 liters of the oil spill; spreading over a 60 km-long area in the Shela and Passur rivers inside Sundarbans, the largest mangrove forest of the country (AFP, 2014).
2.4. Human health effects
Water pollution has increased in both developed and developing countries, threatening the physical and environmental health of billions of people (Javier et al., 2017). About 3.4 million people die worldwide each year from water-related diseases like cholera, typhoid, polio, ascariasis, cryptosporidiosis and diarrheal diseases (UNEP, 2016). Water tainted with defecation puts individuals in danger of contracting cholera, looseness of the bowels, typhoid, and polio (WHO, 2017a,b).
In Bangladesh, every year more than one hundred thousand children under five years old die due to diarrhea-related diseases (Rana, 2009). In 2004 Bangladesh Demographic and Health Survey (BDHS) also reported that 5.1% of deaths of children under five years and 1.2% neonatal deaths were related to diarrhea. Another study reported that 6.9% of deaths of children under five years and 0% neonatal deaths were related to diarrhea (Halder, 2009). Another study reported that 1% neonatal deaths, 15% post-neonatal deaths and 6% under five age children deaths were associated with diarrhea (WHO, 2016). (WHO, 2017a,b) also reported that more than 45,000 under-five youngsters die each year in Bangladesh from diarrhea brought about by sullied water.
Arsenic has been reported as a threat in many parts of the country. Every year, an expected 43,000 individuals die from arsenic harming in the nation. The legislature has made various strides and made strategies to attempt to address the issue. Be that as it may, regardless of a nationwide campaign and social assembly exercises by the legislature and NGOs, information and mindfulness levels among networks stay far beneath desires (Jahan, 2016). Overexposure to arsenic can cause skin lesions, diabetes mellitus, high blood pressure and chronic disease (Yunus et al., 2011). A study collected information from 52 districts of Bangladesh and found that about 40 million people are at risk due to arsenic. They also found that the most common diseases affected by people are melanosis, keratosis, hyperkeratosis, dorsum, gangrene, and skin cancer (Karim, 2000). Another study found that arsenic-related diseases were responsible for 9136 deaths per year in Bangladesh (Alam, 2003). Similarly, another study examined 811 patients with arsenic skin lesions from Pabna, Jessore, Kustia, Chuadanga, Narayanganj and Meherpur districts and found that about 16.6% of those patients had died due to cancer during the last 9–12 years (Chakraborti et al., 2010).
Drinking water polluted by microbial contamination increases the risk of some diseases like typhoid, dysentery, diarrhea, hepatitis A and hepatitis B (Shar et al., 2007). A study found that typhoid, bacillary dysentery, and diarrhea are very common among the bacterial origin waterborne diseases (Parveen, Microbial Contamination of water in around Dhaka city, 2008). Another study revealed that there is a significant correlation between the microbiological quality of water and gastrointestinal diseases (Oguntoke, 2009).
Pesticide contamination in surface water is another threat to public health in Bangladesh. Studies found that pesticide residues can cause nausea, vomiting, blurred vision, coma, difficulty in breathing, deficit hyperactivity disorder in the human body (Rauh et al., 2006). A study found that 26.3%, 24.4% and 18.8% farmers of their study reported excessive sweating, burning eyes and fatigue respectively due to occupational exposure of pesticides (Bhattacharjee, 2013). A daily newspaper published that 11 children were died by diseases which were provoked by pesticides at Dinajpur medical college hospital between May 30 to June 20 (Roy and Karmakar, 2015). Another study reported that many pesticide residues increase the possibility of some diseases like cancer and heart diseases. It also reported that pesticide residues could cause respiratory and neurological damages (Galloway and Handy, 2003). Another study reported that food products containing pesticide residues could cause cancer, teratogenesis and genetic damage (Chowdhury, 2011).
As heavy metals are non-biodegradable, it can show its toxic effect at points which are far from the source of pollution (Tilzer, 1993). Exposure to heavy metals can cause several diseases like kidney damage, cancer, abortion, effect on mind and behavior and sometimes even death in the cases of high exposure (Saha, 2011). Vegetables and fruits contained a high concentration of trace elements like copper, cadmium, and lead which increased the probability of upper gastrointestinal cancer (Türkdoğan et al., 2002). Several studies found different effects of different ions or compounds such as chromium compounds increases the risk of lung cancer (Ishikawa et al., 1994), high consumption of nickel increases the probability of lung and nasal cavity cancer (Ahmed et al., 2015), excessive consumption of zinc can cause electrolyte imbalance, nausea, anemia and lethargy (Prasad, 1984), long term consumption of cadmium increases the rate of kidney failure, softening of bones (Ahmed et al., 2015), and prostate cancer (Gray, 2005).
2.5. Environmental legislation in Bangladesh and it's effectiveness
Water Pollution Control Ordinance 1973 was the first legislation in Bangladesh about water pollution. Then in 1977, Environment Pollution Control Ordinance was declared. Department of Pollution Control Ordinance was organized in 1985 which was renamed as Department of Environment (DoE) afterward. In 1992 another Environmental Policy was declared and The Government of Bangladesh has additionally organized various supplementary arrangements such as the Forest Policy (1994), the Fisheries Policy (1998), the Water Policy (1998), the New Agriculture Extension Policy (1995), the Energy Policy (1995) (Aminuzzaman, 2010).
Bangladesh Environment Conservation Act (ECA), 1995 was passed for the protection of environment models and moderating environmental contamination but the main impediments of the Act are its hushes on the benchmarks, parameters, discharge levels and administration components in view of which the ecological clearance ought to have been connected and gotten (Aminuzzaman, 2010).
The Environmental Conservation Rules, 1997, were proclaimed in promotion of the destinations of the ECA, 1995. As to of poisonous and hazardous substances, the Principles have extensively characterized rules for transfer of waste from various classes of ventures, but it has not indicated the admissible degree of outflows or the commitments of restorative activities (Aminuzzaman, 2010).
Ministry of Water Resources formulated National Water Policy in 1999 to guarantee effective and impartial administration of water assets, appropriate outfitting, and advancement of surface and groundwater, accessibility of water to all concerned, and institutional limit working for water resource administration. The Bangladesh Water Act, 2013 is for the most part given the National Water Policy of 1999, and it is intended for coordinated improvement, administration, appropriation, utilization, security and preservation of water assets in Bangladesh. The demonstration proclaims all type of water inside the region of Bangladesh as the property of the government. Notwithstanding, the surface water in private property can be utilized by the proprietor for all the required reason. The demonstration requires permit for pulling back expansive size of surface or groundwater; notwithstanding, the most significant measure of water that can be pulled back isn't said in the law (BanDuDeltAS, 2015).
Ministry of Environment and Forest formulated the National Environmental Policy 2013 which depends on 17 essential issues and 12 goals pertinent to economic advancement, valuation of environment administrations, sustenance wellbeing, polluter's compensation standard, and adjustment and alleviation to combat environmental change. The activity designs incorporate some new instrument or activities like environmental auditing, agriculture, nearby and national contingency for keeping pollution from sea/water car crash, EIA for lodging and urban advancement ventures, squander heat Recovery activities and so on (BanDuDeltAS, 2015).
Though the defined environment policy genuinely rich in content, it isn't bolstered by essential activities of execution. Several studies reported that the execution of the environmental arrangement and the Environmental Protection Act had been hindered because of some institutional and utilitarian impediments (Khan, 1999; Hanchett, 1997). Different operational guidelines for successful execution of the policy and act would require corresponding and nitty-gritty operational guidelines, a considerable lot of which have not yet been figured. Besides, surges and typhoons are real worries for ecological administration in Bangladesh. However, the Environmental Protection Act still have restricted concern and intercession for such catastrophes. Other problems for a successful execution of environmental policy are insufficient funding, skilled human, lack of inter-agency relation, irregularity with different policies, absence of inter-sectoral arrangement, lack of administrative and institutional capacity, impediments of the environment laws, Outdated environmental laws as well as ignorance about these laws, non-punitive approach of laws, political corruption and so on (Aminuzzaman, 2010).
3. Conclusion
The present investigation demonstrates that most of the water bodies in Bangladesh are contaminated with several contaminants and not suitable for human consumption without proper treatment. Besides heavy metal contamination, pesticide contamination of surface water sources is the most prospective menace for the people of Bangladesh. Bacteriological contamination is also a great source of surface water which causes threats to both urban and rural people. Among the heavy metals, Arsenic found in groundwater at an alarming rate all over the country. High level of iron, chromium, nickel, and lead is also worrying. Copper, zinc, and manganese are found below the standards limit in most of the sources. In addition, most of the cations like Na+, K+, Ca2+, Mg2+ found in water sources are mostly below the standards limit. Lack of proper monitoring, laws implementation, adequate human resources as well as lack of modern treatment plants and water supply systems, and poor awareness and education about water use and safety are the main prompt of water pollution in Bangladesh. There are little records mainly longitudinal data about water-borne diseases in the nation, so more surveys need to be done to get a better idea of water-related diseases.
Declarations
Author contribution statement
All authors listed have significantly contributed to the development and the writing of this article.
Funding statement
This research did not receive any specific grant from funding agencies in the public, commercial, or not-for-profit sectors.
Competing interest statement
The authors declare no conflict of interest.
Additional information
No additional information is available for this paper.
References
- Acharjee M.R. Microbiological study on supply water and treated water in Dhaka city. Stamford J. Microbiol. 2011;1(1):42–45. [Google Scholar]
- Acharjee M., Rahman F., Jahan F., Noor R. Bacterial proliferation in municipal water supplied in mirpur locality of Dhaka city, Bangladesh. Clean Soil Air Water. 2014;42(4):434–441. [Google Scholar]
- Afful S.A.-A. Spectrum of organochlorine pesticide residues in fish samples from the Densu Basin. Res. J. Environ. Earth Sci. 2010;2(3):133–138. [Google Scholar]
- Ahmed F., Bibi M.H., Ishiga H., Fukushima T., Maruoka T. Geochemical study of arsenic and other trace elements in groundwater and sediments of the Old Brahmaputra River Plain, Bangladesh. Environ. Earth Sci. 2010;60(6):1303–1316. [Google Scholar]
- Ahmed M.J., Haque M.R., Rahman M.M. Physicochemical assessment of surface and groundwater resources of Noakhali region of Bangladesh. Int. J. Chem. Sci. Technol. 2011;1(1):1–10. [Google Scholar]
- Ahmed M.K., Ahmed S., Rahman S., Haque M.R., Islam M.M. Heavy metals concentration in water, sediments and their bioaccumulations in some freshwater fishes and mussel in Dhaleshwari River, Bangladesh. Terr. Aquat. Environ. Toxicol. 2009;3(1):33–41. [Google Scholar]
- Ahmed M.K., Baki M.A., Islam M.S., Kundu G.K., Habibullah-Al-Mamun M., Sarkar S.K., Hossain M.M. Human health risk assessment of heavy metals in tropical fish and shellfish collected from the river Buriganga, Bangladesh. Environ. Sci. Pollut. Control Ser. 2015 doi: 10.1007/s11356-015-4813-z. [DOI] [PubMed] [Google Scholar]
- Ahmed M.K., Das M., Islam M.M., Akter M.S., Islam S., Al-Mansur M.A. Physico-chemical properties of tannery and textile effluents and. World Appl. Sci. J. 2011;12(2):152–159. [Google Scholar]
- Ahmed W.Y. Fecal indicators and bacterial pathogens in bottled water from Dhaka, Bangladesh. Braz. J. Microbiol. 2013;44(1):97–103. doi: 10.1590/S1517-83822013005000026. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Akter K., Kurisu K., Hanaki K. Water use and pollution recognition from the viewpoint of local residents in Dhaka, Bangladesh. Water. 2017;9:331. [Google Scholar]
- Alam M.G. Arsenic and heavy metal contamination of vegetables grown in Samta village, Bangladesh. Sci. Total Environ. 2003;308:83–96. doi: 10.1016/S0048-9697(02)00651-4. [DOI] [PubMed] [Google Scholar]
- Alam M.J., Islam M.R., Muyen Z., Mamun M., Islam S. Water quality parameters along rivers. Int. J. Environ. Sci. Technol. 2007;4(1):159–167. [Google Scholar]
- Alam M.S. Toxigenic Vibrio cholerae in the aquatic environment of mathbaria, Bangladesh. Appl. Environ. Microbiol. 2006;72(4):2849–2855. doi: 10.1128/AEM.72.4.2849-2855.2006. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Alam G.M. International Conference on Mechanical Engineering 2009. 2009. Environmental pollution of Bangladesh – it’s effect and control; pp. 1–7. Dhaka. [Google Scholar]
- Albert M.J. Prevalence of enterotoxin genes in Aeromonas spp. isolated from children with diarrhea, healthy controls, and the environment. J. Clin. Microbiol. 2000;38(10):3785–3790. doi: 10.1128/jcm.38.10.3785-3790.2000. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Ali M.M., Ali M.L., Islam M.S., Rahman M.Z. Preliminary assessment of heavy metals in water and sediment of Karnaphuli River, Bangladesh. Environ. Nanotechnol. Monit. Manag. 2016;5:27–35. [Google Scholar]
- Amin F.B. 2015, March 24. Water Pollution of Most of the Water Sources in Bangladesh.http://fairbd.net/water-pollution-of-most-of-the-water-sources-in-bangladesh/ Retrieved from Fairbd: [Google Scholar]
- Aminuzzaman S.M. South Asia Climate Change Forum, Organized by Monash Sustainability Institute. Monash University, Australia; Melbourne: 2010. Environment policy of Bangladesh: a case study of an ambitious policy with implementation snag; pp. 1–18. [Google Scholar]
- Anonymous . Parliamentary Standing Committee on Ministry of Environment and Forest; Dhaka: 2010. Pollution Abatement Strategies for Rivers and Wet Lands in and around Dhaka City. [Google Scholar]
- Anwar A.H., Saing L.A. Aquifer vulnerability to pesticide leaching and its impact on groundwater. J. Environ. Res. Dev. 2010;5(1):12–22. [Google Scholar]
- Aranda P.R., Moyano S., Martinez L.D., Vito I.E. Determination of trace chromium(VI) in drinking water using X-ray fluorescence spectrometry after solid-phase extraction. Anal. Bioanal. Chem. 2010;398(2):1043–1048. doi: 10.1007/s00216-010-3950-y. [DOI] [PubMed] [Google Scholar]
- Askary V.R., Jahan N.A., Sabbagh A., Jahani F.S., Dourandish N., Kamachali A.R. A potential medicinal importance of zinc in human health and chronic diseases. Clin. Biochem. 2011;44(13) Supp-S. [Google Scholar]
- Azizullah A., Khattak M.N., Richter P., Häder D.-P. Water pollution in Pakistan and its impact on public health — a review. Environ. Int. 2011;37:479–497. doi: 10.1016/j.envint.2010.10.007. [DOI] [PubMed] [Google Scholar]
- Bagchi S.A.-R. Quantitative analysis of pesticide residues in some pond water samples of Bangladesh. Asian J. Water Environ. Pollut. 2009;6(4):27–30. [Google Scholar]
- Bal W., Kozłowski H., Kasprzak K.S. Molecular models in nickel carcinogenesis. J. Inorg. Biochem. 2000;79(1-4):213–218. doi: 10.1016/s0162-0134(99)00169-5. [DOI] [PubMed] [Google Scholar]
- BanDuDeltAS . General Economics Division, Planning Commission, Government of Bangladesh; Dhaka: 2015. Environmental Pollution. [Google Scholar]
- Banglapedia . 2019, 03 23. River.http://en.banglapedia.org/index.php?title=River Retrieved from Banglapedia: [Google Scholar]
- Banu Z., Chowdhury M.S., Hossain M.D., Nakagami K. Contamination and ecological risk assessment of heavy metal in the sediment of Turag river, Bangladesh: an index analysis approach. J. Water Resour. Prot. 2013:239–248. [Google Scholar]
- Baron S. fourth ed. University of Texas Medical Branch at Galveston; 1996. Medical Microbiology. [PubMed] [Google Scholar]
- BBS/UNICEF . Bangladesh Bureau of Statistics/UNICEF; Dhaka: 2010. Multiple Indicator Cluster Survey 2009: Volume 1, Technical Report. [Google Scholar]
- BBS/UNICEF . Bangladesh Bureau of Statistics/UNICEF; Dhaka: 2011. Bangladesh National Drinking Water Quality Survey of 2009. [Google Scholar]
- Bempah C.K.-F. A preliminary assessment of consumer’s exposure to organochlorine pesticides in fruits and vegetables and the potential health risk in Accra Metropolis, Ghana. Food Chem. 2011;128(4):1058–1065. [Google Scholar]
- Bhattacharjee S.C. Impacts of pesticide exposure on paddy farmers’ health. Jahangirnagar Univ. Environ. Bull. 2013;2:18–25. [Google Scholar]
- Bhattacharjee S., Fakhruddin A., Chowdhury M., Rahman M., Alam M. Monitoring of selected pesticides residue levels in water samples of cultivated lands and removal of cypermethrin and chlorpyrifos residues from water using rice bran. Bull. Environ. Contam. Toxicol. 2012;89(2):348–353. doi: 10.1007/s00128-012-0686-8. [DOI] [PubMed] [Google Scholar]
- Bhattacharya P., Hasan M.A., Sracek O., Smith E., Ahmed K.M., Brömssen M.v. Groundwater chemistry and arsenic mobilization in the Holocene flood plains in south-central Bangladesh. Environ. Geochem. Health. 2009;31(1):23–43. doi: 10.1007/s10653-008-9230-5. [DOI] [PubMed] [Google Scholar]
- Bhuiyan M.A., Bodrud-Doza M., Islam A.R., Rakib M.A., Rahman M.S., Ramanathan A.L. Assessment of groundwater quality of Lakshimpur district of Bangladesh using water quality indices, geostatistical methods, and multivariate analysis. Environ. Earth Sci. 2016;75(12):1020. [Google Scholar]
- Bhuiyan M.A., Dampare S.B., Islam M.A., Suzuki S. Source apportionment and pollution evaluation of heavy metals in water and sediments of Buriganga River, Bangladesh, using multivariate analysis and pollution evaluation indices. Environ. Monit. Assess. 2015;187(1):4075. doi: 10.1007/s10661-014-4075-0. [DOI] [PubMed] [Google Scholar]
- Bhuiyan M.A., Islam M., Dampare S.B., Parvez L., Suzuki S. Evaluation of hazardous metal pollution in irrigation and drinking water systems in the vicinity of a coal mine area of northwestern Bangladesh. J. Hazard Mater. 2010;179(3):1065–1077. doi: 10.1016/j.jhazmat.2010.03.114. [DOI] [PubMed] [Google Scholar]
- Bhuiyan M.A., Rakib M.A., Dampare S.B., Ganyaglo S., Suzuki S. Surface water quality assessment in the central part of Bangladesh using multivariate analysis. KSCE J. Civil Eng. 2011;15(6):995–1003. [Google Scholar]
- Bhuiyan N.H. Organochlorine insecticides (DDT and heptachlor) in dry fish available in Bangladesh: seasonal trends and species variability. J. Chil. Chem. Soc. 2009;54(3):278–281. [Google Scholar]
- Bodrud-Doza M., Islam A.T., Ahmed F., Das S., Saha N., Rahman M.S. Characterization of groundwater quality using water evaluation indices, multivariate statistics and geostatistics in central Bangladesh. Water Science. 2016;30(1):19–40. [Google Scholar]
- Bogden J.D. Humana Press; New York: 2000. Clinical Nutrition of the Essential Trace Elements and Minerals: the Guide for Health Professionals. [Google Scholar]
- Botkin D.B., Keller E.A. Environmental Science: Earth as a Living Planet. 8 ed. John Wiley & Sons, Inc; 2011. Water pollution and treatme; pp. 400–401. [Google Scholar]
- Bremner I., Beattie J.H. Metallothionein and the trace minerals. Annu. Rev. Nutr. 1990;10(1):63–83. doi: 10.1146/annurev.nu.10.070190.000431. [DOI] [PubMed] [Google Scholar]
- Casey J.R. Why bicarbonate? Biochem. Cell Biol. 2006;84(6):930–939. doi: 10.1139/o06-184. [DOI] [PubMed] [Google Scholar]
- Cempel M., Nikel G. Nickel: a review of its sources and environmental. Pol. J. Environ. Stud. 2005;15(3):375–382. [Google Scholar]
- Chakraborti D., Rahman M.M., Das B., Murrill M., Dey S., Mukherjee S.C. Status of groundwater arsenic contamination in Bangladesh: a 14-year study report. Water Res. 2010;44(19):5789–5802. doi: 10.1016/j.watres.2010.06.051. [DOI] [PubMed] [Google Scholar]
- Chakraborti D., Rahman M.M., Mukherjee A., Alauddin M., Hassan M., Dutta R.N. Groundwater arsenic contamination in Bangladesh—21 Years of research. J. Trace Elem. Med. Biol. 2015;31:237–248. doi: 10.1016/j.jtemb.2015.01.003. [DOI] [PubMed] [Google Scholar]
- Chowdhury A.Z., Islam M.N., Moniruzzaman M., Gan S.H., Alam M.K. Organochlorine insecticide residues are found in surface, irrigated water samples from several districts in Bangladesh. Bull. Environ. Contam. Toxicol. 2013;90(2):149–154. doi: 10.1007/s00128-012-0897-z. [DOI] [PubMed] [Google Scholar]
- Chowdhury A.Z., Jahan S.A., Islam M.N., Moniruzzaman M., Alam M.K., Zaman M.A. Occurrence of organophosphorus and carbamate pesticide residues in surface water samples from the Rangpur district of Bangladesh. Bull. Environ. Contam. Toxicol. 2012;89(1):202–207. doi: 10.1007/s00128-012-0641-8. [DOI] [PubMed] [Google Scholar]
- Chowdhury M.A. Organophosphorus and carbamate pesticide residues detected in water samples collected from paddy and vegetable fields of the Savar and Dhamrai Upazilas in Bangladesh. Int. J. Environ. Res. Public Health. 2012;9(9):3318–3329. doi: 10.3390/ijerph9093318. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Chowdhury N.T. Water management in Bangladesh: an analytical review. Water Policy. 2010;12(1):32. [Google Scholar]
- Chowdhury M.T. Chlorinated pesticide residue status in tomato, potato and carrot. J. Exp. Sci. 2011;2(1):01–05. [Google Scholar]
- Chowdhury M.T. Chlorinated pesticide residue status in some winter vegetables. Intl. J. Agric. Crop Sci. 2013;6(11):667–675. [Google Scholar]
- Chowdhury N.S., Clemett A.E. MACH technical report; Dhaka: 2006. Industrial Pollution and its Threat to Mokesh Beel Wetland in Kaliakoir. [Google Scholar]
- Chung P.Y. The emerging problems of Klebsiella pneumoniae infections: carbapenem resistance and biofilm formation. FEMS Microbiol. Lett. 2016;363(20):1–6. doi: 10.1093/femsle/fnw219. [DOI] [PubMed] [Google Scholar]
- Cunningham W.P., Cunningham M.A. Environmental Science: A Global Concern. 11 ed. McGraw-Hill Companies, Inc; New York: 2011. Water pollution; pp. 397–398. [Google Scholar]
- Das H., Mitra A., Sengupta P., Hossain A., Islam F., Rabbani G. Arsenic concentrations in rice, vegetables, and fish in Bangladesh: a preliminary study. Environ. Int. 2004;30(3):387. doi: 10.1016/j.envint.2003.09.005. [DOI] [PubMed] [Google Scholar]
- Dasgupta S.M. A pinch or a pint? Evidence of pesticide overuse in Bangladesh. J. Agric. Econ. 2007;58(1):91–114. [Google Scholar]
- De Gheldre Y.V. Molecular epidemiology of an outbreak of multidrug-resistant Enterobacter aerogenes infections and in vivo emergence of imipenem resistance. J. Clin. Microbiol. 1997;35(1):152–160. doi: 10.1128/jcm.35.1.152-160.1997. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Demira V., Erginc S., Cakιra Y., Celika F. Determination and Health Risk Assessment of Heavy Metals. Water Resour. 2015:508–516. [Google Scholar]
- DoE . Depertment of Environment, Ministry of Environment and Forest, Bangladesh; Dhaka: 2008. Guide for Assessment of Effluent Treatment Plants. [Google Scholar]
- DoE . Ministry of Environment & Forest, Government of Bangladesh; Dhaka: 2014. River Water Quality Report 2014. [Google Scholar]
- DPHE . 2018. Department of Public Health Engineering, Government of Bangladesh.http://old.dphe.gov.bd/index.php?option=com_content&view=article&id=125&Itemid=133 Retrieved July 31, 2019, from. [Google Scholar]
- Driscoll T., Steenland K., Prüss-Üstün A., Nelson D.I., Leigh J. In: Annette Prüss-Üstün D.C.-L., editor. Vol. 6. World Health Organization; 2004. (Occupational Carcinogens: Assessing the Environmental burden of Disease at National and Local Levels). [Google Scholar]
- El-Mekkawi H.D. Determination of chlorinated organic pesticide residues in water, sediments and fish from private fish farms at Abbassa and Sahl Al-Husainia, Sharkia Governorate. Aust. J. Basic Appl. Sci. 2009;3(4):4376–4383. [Google Scholar]
- Ercumen A.,N.A. Effects of source- versus household contamination of tubewell water on child diarrhea in rural Bangladesh: a randomized controlled trial. PLoS One. 2015 doi: 10.1371/journal.pone.0121907. [DOI] [PMC free article] [PubMed] [Google Scholar]
- FAO . UN Water; 2007. Coping with Water Scarcity: Challenge of the Twenty-First century. [Google Scholar]
- Farooqui A.K. Investigation of a community outbreak of typhoid fever associated with drinking water. BMC Public Health. 2009;476 doi: 10.1186/1471-2458-9-476. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Fatema M.R. Residues of insecticide in farm and market samples of Eggplant in Bangladesh. J. Entomol. Zool. Stud. 2013;1(6):147–150. [Google Scholar]
- Fazal M.A., Kawachi T., Ichion E. Extent and severity of groundwater arsenic. Water Int. 2001;26(3):370–379. [Google Scholar]
- Felmingham D.W. Enterococcus species in urinary tract infection. Clin. Infect. Dis. 1992;15(2):295–301. doi: 10.1093/clinids/15.2.295. [DOI] [PubMed] [Google Scholar]
- Ferguson A.S. Comparison of fecal indicators with pathogenic bacteria and rotavirus in groundwater. Sci. Total Environ. 2012;431:314–322. doi: 10.1016/j.scitotenv.2012.05.060. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Ferguson A.S., Mailloux B.J., Ahmed K.M., van Geen A., McKay L.D., Culligan P.J. Hand-pumps as reservoirs for microbial contamination of well water. J. Water Health. 2011;9(4):708–717. doi: 10.2166/wh.2011.106. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Fewtrell L. Drinking-water nitrate, methemoglobinemia, and global burden of disease: a discussion. Environ. Health Perspect. 2004;112(14):1371–1374. doi: 10.1289/ehp.7216. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Flanagan S., Johnston R., Zheng Y. Arsenic in tube well water in Bangladesh: health and economic impacts and implications for arsenic mitigation. Bull. World Health Organ. 2012;90(11):839–846. doi: 10.2471/BLT.11.101253. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Flora G., Gupta D., Tiwari A. Toxicity of lead: a review with recent updates. Interdiscip. Toxicol. 2012;5(2):47–58. doi: 10.2478/v10102-012-0009-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Frisbie S.H. The concentrations of arsenic and other toxic elements in Bangladesh’s drinking water. Environ. Health Perspect. 2002;110(11):1147–1153. doi: 10.1289/ehp.021101147. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Galloway T., Handy R. Immunotoxicity of organophosphorous pesticides. Ecotoxicology. 2003;12(1–4):345–363. doi: 10.1023/a:1022579416322. [DOI] [PubMed] [Google Scholar]
- Geldreich E.E. CRC Press; 1996. Microbial Quality of Water Supply in Distribution Systems. [Google Scholar]
- Goad R.T. Carbofuran-induced endocrine disruption in adult male rats. Toxicol. Mech. Methods. 2004;14(4):233–239. doi: 10.1080/15376520490434476. [DOI] [PubMed] [Google Scholar]
- Goldhaber S.B. Trace element risk assessment: essentiality vs. toxicity. Regul. Toxicol. Pharmacol. 2003;38(2):232–242. doi: 10.1016/s0273-2300(02)00020-x. [DOI] [PubMed] [Google Scholar]
- Gray M.A. 2005. The role of Cadmium, Zinc, and Selenium in Prostate Disease. Metal Contaminants in New Zealand: Sources, Treatments, and Effects on Ecology and Human Health; pp. 393–414. [Google Scholar]
- Grollman A. The role of salt in health and disease. Am. J. Cardiol. 1961;8(4):593–601. [PubMed] [Google Scholar]
- Gupta U.C., Gupta S.C. Trace element toxicity relationships to crop production and livestock and human health: implications for management. Commun. Soil Sci. Plant Anal. 1998;29(11–14):1491–1522. [Google Scholar]
- Halder A.K. Causes of early childhood deaths in urban Dhaka, Bangladesh. PLoS One. 2009;4(12):1–7. doi: 10.1371/journal.pone.0008145. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Halim M.A., Majumder R.K., Nessa S.A., Oda K., Hiroshiro Y., Jinno K. Arsenic in shallow aquifer in the eastern region of Bangladesh: insights from principal component analysis of groundwater compositions. Environ. Monit. Assess. 2010;161(1-4):453–472. doi: 10.1007/s10661-009-0760-9. [DOI] [PubMed] [Google Scholar]
- Halim M.A., Majumder R.K., Nessa S.A., Oda K., Hiroshiro Y., Saha B.B. Groundwater contamination with arsenic in Sherajdikhan, Bangladesh: geochemical and hydrological implications. Environ. Geol. 2009;58(1):73–84. [Google Scholar]
- Halim M.A., Majumder R.K., Rasul G., Hirosiro Y., Sasaki K., Shimada J., Jinno K. Geochemical evaluation of arsenic and manganese in shallow groundwater and core sediment in Singair Upazila, Central Bangladesh. Arabian J. Sci. Eng. 2014;39(7):5585–5601. [Google Scholar]
- Hanchett S. Participation and policy development: the case of the Bangladesh flood action plan. Dev. Policy Rev. 1997;15(3):277–295. [Google Scholar]
- Harris Z.L., Gitlin J.D. Genetic and molecular basis for copper toxicity. Am. J. Clin. Nutr. 1996;63:836S–841S. doi: 10.1093/ajcn/63.5.836. [DOI] [PubMed] [Google Scholar]
- Harrison R. fourth ed. Royal Society of Chemistry; Cambridge: 2001. Pollution: Causes, Effects and Control. [Google Scholar]
- Hasan A.B., Kabir S., Selim Reza A., Zaman M.N., Ahsan M.A., Akbor M.A., Rashid M.M. Trace metals pollution in seawater and groundwater in the ship breaking area of Sitakund Upazilla, Chittagong, Bangladesh. Mar. Pollut. Bull. 2013;71(1-2):317–324. doi: 10.1016/j.marpolbul.2013.01.028. [DOI] [PubMed] [Google Scholar]
- Hasan M.K., Khan M.R., Nesha M.K., Happy M.A. Analysis of water quality using chemical. Open J. Water Pollut. Treat. 2014;1(2):58–74. [Google Scholar]
- Hasanuzzaman M., Rahman M.A., Salam M.A. Identification and quantification of pesticide residues in water samples of Dhamrai Upazila, Bangladesh. Appl. Water Sci. 2016 [Google Scholar]
- Hayat K.A. Determination of pesticide residues in blood samples of villagers involved in pesticide application at District Vehari (Punjab), Pakistan. Afr. J. Environ. Sci. Technol. 2010;4(10):666–684. [Google Scholar]
- He F.J., MacGregor G.A. Beneficial effects of potassium on human health. Physiol. Plant. 2008;133(4):725–735. doi: 10.1111/j.1399-3054.2007.01033.x. [DOI] [PubMed] [Google Scholar]
- Heaney R.P., Gallagher J.C., Johnston C.C., Neer R., Parfitt A.M., Whedon G.D. Calcium nutrition and bone health in the elderly. Am. J. Clin. Nutr. 1982;36:986–1013. doi: 10.1093/ajcn/36.5.986. [DOI] [PubMed] [Google Scholar]
- Heizer W.D., Sandler R.S., Seal E., Murray S.C., Busby M.G., Schliebe B.G., Pusek S.N. Intestinal effects of sulfate in drinking water on normal human subjects. Dig. Dis. Sci. 1997;42(5):1055–1061. doi: 10.1023/a:1018801522760. [DOI] [PubMed] [Google Scholar]
- Herrington D.A. Toxin, toxin-coregulated pili, and the toxR regulon are essential for Vibrio cholerae pathogenesis in humans. J. Exp. Med. 1988;168(4):1487–1492. doi: 10.1084/jem.168.4.1487. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Hooper P.L. Zinc lowers high-density lipoprotein-cholesterol levels. JAMA, J. Am. Med. Assoc. 1980;244(17):1960. [PubMed] [Google Scholar]
- Hossain G., Howladar M.F., Nessa L., Ahmed S.S., Quamruzzaman C. Hydrochemistry and classification of groundwater resources of ishwardi municipal area, Pabna district, Bangladesh. Geotech. Geol. Eng. 2010;28(5):671–679. [Google Scholar]
- Hossain M.S., Chowdhury M.A., Pramanik M.K., Rahman M.A., Fakhruddin A.N., Alam M.K. Determination of selected pesticides in water samples adjacent to agricultural fields and removal of organophosphorus insecticide chlorpyrifos using soil bacterial isolates. Appl. Water Sci. 2015;5(2):171–179. [Google Scholar]
- Ishikawa Y., Nakagawa K., Satoh Y., Kitagawa T., Sugano H., Hirano T., Tsuchiya E. Characteristics of chromate workers' cancers, chromium lung deposition and precancerous bronchial lesions: an autopsy study Nature Publishing. Br. J. Canc. 1994;70(1):160–166. doi: 10.1038/bjc.1994.268. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Islam A.R., Ahmed N., Bodrud-Doza M., Chu R. Characterizing groundwater quality ranks for drinking purposes in Sylhet district, Bangladesh, using entropy method, spatial autocorrelation index, and geostatistics. Environ. Sci. Pollut. Control Ser. 2017 doi: 10.1007/s11356-017-0254-1. [DOI] [PubMed] [Google Scholar]
- Islam A.R., Shen S., Bodrud-Doza M., Atiqur Rahman M., Das S. Assessment of trace elements of groundwater and their spatial distribution in Rangpur district, Bangladesh. Arab. J. Geosci. 2017;10(4):95. [Google Scholar]
- Islam A.R., Shen S., Haque M.A., Bodrud-Doza M., Maw K.W., Habib M.A. Assessing groundwater quality and its sustainability in Joypurhat district of Bangladesh using GIS and multivariate statistical approaches. Environ. Dev. Sustain. 2017 [Google Scholar]
- Islam M.A. Bacteriological assessment of drinking water supply options in coastal areas of Bangladesh. J. Water Health. 2011;9(2):415–428. doi: 10.2166/wh.2011.114. [DOI] [PubMed] [Google Scholar]
- Islam M.A., Zahid A., Rahman M.M., Rahman M.S., Islam M.J., Akter Y. Investigation of groundwater quality and its suitability for drinking and agricultural use in the south central part of the coastal region in Bangladesh. Water Qual. Expo. Health. 2017;9(1):27–41. [Google Scholar]
- Islam M.N. Monitoring of organochlorine pesticide residues in surface water samples of the agricultural field of Bangladesh. J. Subtrop. Agric. Res. Dev. 2007;5(5):357–360. [Google Scholar]
- Islam M.R. 2010 April 24. A Silent Icy River in Dhaka!http://www.thedailystar.net/news-detail-135603 Retrieved from The Daily Star: [Google Scholar]
- Islam M.R., Salminen R., Lahermo P.W. Arsenic and other toxic elemental contamination of groundwater, surface water and soil in Bangladesh and its possible effects on human health. Environ. Geochem. Health. 2000;22:33–53. [Google Scholar]
- Islam M.S. Faecal pollution of freshwater environments in Bangladesh. Int. J. Environ. Stud. 1994;46(2–3):161–165. [Google Scholar]
- Islam M.S., Ahmed M.K., Habibullah-Al-Mamun M., Hoque M.F. Preliminary assessment of heavy metal contamination in surface sediments from a river in Bangladesh. Environ. Earth Sci. 2015;73(4):1837–1848. [Google Scholar]
- Islam M.S., Ahmed M.K., Raknuzzaman M., Habibullah -Al- Mamun M., Islam M.K. Heavy metal pollution in surface water and sediment: a preliminary assessment of an urban river in a developing country. Ecol. Indicat. 2015;48:282–291. [Google Scholar]
- Islam M.S., Siddika A., Khan M.N., Goldar M.M., Sadique M.A., Kabir A.N. Microbiological analysis of tube-well water in a rural area of Bangladesh. Appl. Environ. Microbiol. 2001;67(7):3328–3330. doi: 10.1128/AEM.67.7.3328-3330.2001. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Islam S.B. Bacteriological safety assessment of municipal tap water and quality of bottle water in Dhaka city: health hazard analysis. Bangladesh J. Med. Microbiol. 2010;4(1):9–13. [Google Scholar]
- Islam S.M.-U., Bhuiyan M.A., Rume T., Azam G. Hydrogeochemical investigation of groundwater in shallow coastal aquifer of Khulna District, Bangladesh. Appl. Water Sci. 2017;7(8):4219–4236. [Google Scholar]
- Islam S.M.-U., Majumder R.K., Uddin M.J., Khalil M.I., Alam M.F. Hydrochemical characteristics and quality assessment of groundwater in patuakhali district, southern coastal region of Bangladesh. Water Qual. Expo. Health. 2017;9(1):43–60. [Google Scholar]
- IWM . World Bank; Dhaka: 2007. Industrial Environmental Compliance and Pollution. [Google Scholar]
- IWM . 2009. Final Report: Hydro-Geological Study and Mathematical Modelling to Identify Sites for Installation of Observation Well Nests, Selection of Model Boundary, Supervision of Pumping Test, Slug Test, Assessment of Different Hydro-Geological Parameters Collecti. Dhaka. [Google Scholar]
- Izah S.C., Chakrabarty N., Srivastav A.L. A review on heavy metal concentration in potable water. Water Qual. Expo. Health. 2016;8(2):285–304. [Google Scholar]
- Jahan H. 2016, 10 18. Arsenic in Bangladesh: How to Protect 20 Million from the World's Largest Poisoning.www.theguardian.com/global-development-professionals-network/2016/oct/18/arsenic-contamination-poisoning-bangladesh-solutions Retrieved from The Guardian: [Google Scholar]
- Javier M.-S., Sara M.Z., Hugh T. 2017. Water Pollution from Agriculture: a Global Review. Rome, Colombo: the Food and Agriculture Organization of the United Nations, International Water Management Institute on Behalf of. [Google Scholar]
- Jihen E.H., Imed M., Fatima H., Abdelhamid K. Protective effects of selenium (Se) and zinc (Zn) on cadmium (Cd) toxicity in the liver and kidney of the rat: histology and Cd accumulation. Food Chem. Toxicol. 2008;46(11):3527. doi: 10.1016/j.fct.2008.08.037. [DOI] [PubMed] [Google Scholar]
- Johnson C.J., Kross B.C. Continuing importance of nitrate contamination of groundwater and wells in rural areas. Am. J. Ind. Med. 1990;18(4):449–456. doi: 10.1002/ajim.4700180416. [DOI] [PubMed] [Google Scholar]
- Jonnalagadda S., Mhere G. Water quality of the odzi river in the eastern highlands of Zimbabwe. Water Res. 2001;35(10):2376. doi: 10.1016/s0043-1354(00)00533-9. [DOI] [PubMed] [Google Scholar]
- Kamal D., Khan A., Rahman M., Ahamed F. Study on the physico chemical properties of water of Mouri River, Khulna, Bangladesh. Pak. J. Biol. Sci. 2007;10(5):710–717. doi: 10.3923/pjbs.2007.710.717. [DOI] [PubMed] [Google Scholar]
- Kamal M.M., Malmgren-Hansen A., Badruzzaman A. Assessment of pollution of the River Buriganga, Bangladesh, using a water quality model. Water Sci. Technol. 1999;40(2):129–136. [Google Scholar]
- Kamrin M.A. CRC press; 1997. Pesticide Profiles: Toxicity, Environmental Impact, and Fate. [Google Scholar]
- Karim M.M. Arsenic in groundwater and health problems in Bangladesh. Water Res. 2000;34(1):304–310. [Google Scholar]
- Karn S., Harada H. Surface water pollution in three urban territories of Nepal, India, and Bangladesh. Environ. Manag. 2001;28(4):483–496. doi: 10.1007/s002670010238. [DOI] [PubMed] [Google Scholar]
- Kelly W.R., Panno S.V., Hackley K. Illinois State Water Survey, Prairie Research Institute, University of Illinois at Urbana-Champaign; Champaign, Illinois: 2012. The Sources, Distribution, and Trends. [Google Scholar]
- Khan N.A. The politics of the Bangladesh environmental protection act. Environ. Pol. 1999;8(1):311–317. [Google Scholar]
- Kondakis X.G., Makris N., Leotsinidis M., Prinou M., Papapetropoulos T. Possible health effects of high manganese concentration in drinking water. Arch. Environ. Health. 1989;44(3):175–178. doi: 10.1080/00039896.1989.9935883. [DOI] [PubMed] [Google Scholar]
- Kreuger J. Pesticides in stream water within an agricultural catchment in southern Sweden. Sci. Total Environ. 1998;216(3):227–251. doi: 10.1016/s0048-9697(98)00155-7. [DOI] [PubMed] [Google Scholar]
- Leeuwen F.X. Safe drinking water: the toxicologist's. Food Chem. Toxicol. 2000;38:S51–S58. doi: 10.1016/s0278-6915(99)00140-4. [DOI] [PubMed] [Google Scholar]
- Lindsay E.R., Maathuis F.J. New molecular mechanisms to reduce arsenic in crops. Trends Plant Sci. 2017;22(12):1016–1026. doi: 10.1016/j.tplants.2017.09.015. [DOI] [PubMed] [Google Scholar]
- Luby S., Gupta S., Sheikh M., Johnston R., Ram P., Islam M. Tubewell water quality and predictors of contamination in three flood-prone areas in Bangladesh. J. Appl. Microbiol. 2008;105(4):1002–1008. doi: 10.1111/j.1365-2672.2008.03826.x. [DOI] [PubMed] [Google Scholar]
- Majumder A. 2009, May 19. Bangladesh River Pollution Threatens Millions.https://www.reuters.com/article/us-bangladesh-rivers/bangladesh-river-pollution-threatens-millions-idUSTRE54I04G20090519 Retrieved from Reuters: [Google Scholar]
- Map O.T. 2019, 03 23. Large Detailed Map of Bangladesh with Cities.http://ontheworldmap.com/bangladesh/large-detailed-map-of-bangladesh-with-cities.html Retrieved from On The World Map: [Google Scholar]
- Matin M., Malek M., Amin M., Rahman S., Khatoon J., Rahman M. Organochlorine insecticide residues in surface and underground water from different regions of Bangladesh. Agric. Ecosyst. Environ. 1998;69(1):11–15. [Google Scholar]
- Meisner C. Development Economics Research Group, Infrastructure and Environment Department, The World Bank; Dhaka: 2004. Report of Pesticide Hotspots in Bangladesh. [Google Scholar]
- Mekonnen M.M., Hoekstra A.Y. Four billion people facing severe water scarcity. Sci. Adv. 2016;2(2) doi: 10.1126/sciadv.1500323. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Miah S.J. Unsafe use of pesticide and its impact on health of farmers: a case study in Burichong Upazila, Bangladesh. IOSR J. Environ. Sci. Toxicol. Food Technol. 2014;8(1):57–67. [Google Scholar]
- Miller G.T., Spoolman S.E. Environmental Science. fifteenth ed. Cengage Learning; Boston: 2016. Water resources and water pollution; pp. 268–269. [Google Scholar]
- Milman N., Pedersen P., Steig T.á., Byg K.-E., Graudal N., Fenger K. Clinically overt hereditary hemochromatosis in Denmark 1948–1985: epidemiology, factors of significance for long-term survival, and causes of death in 179 patients. Ann. Hematol. 2001;80(12):737–744. doi: 10.1007/s002770100371. [DOI] [PubMed] [Google Scholar]
- Mokaddes M.A., Nahar B.S., Baten M. Status of heavy metal contaminations of lake water of Dhaka. J. Environ. Sci. Nat. Res. 2013;6(1):345–348. [Google Scholar]
- Mondol M.N., Chamon A.S., Faiz B., Elahi S.F. Seasonal variation of heavy metal concentrations in water and plant samples around tejgaon industrial area of Bangladesh. J. Bangladesh Acad. Sci. 2011;35(1):19–41. [Google Scholar]
- Mostafa M.G., Uddin S.M., Haque A.B. Assessment of hydro-geochemistry and groundwater quality of Rajshahi City in Bangladesh. Appl. Water Sci. 2017 [Google Scholar]
- Nahar M.S., Zhang J., Ueda A., Yoshihisa F. Investigation of severe water problem in urban areas of a developing country: the case of Dhaka, Bangladesh. Environ. Geochem. Health. 2014;36(6):1079–1094. doi: 10.1007/s10653-014-9616-5. [DOI] [PubMed] [Google Scholar]
- Nahar N.M. Analysis of pesticide residues in some local fish and vegetable. Dhaka Univ. J. Sci. 2008;56(2):1–4. [Google Scholar]
- Nielsen G.D., Søderberg U., Jørgensen P.J., Templeton D.M., Rasmussen S.N., Andersen K.E., Grandjean P. Absorption and retention of nickel from drinking water in relation to food intake and nickel sensitivity. Toxicol. Appl. Pharmacol. 1999;154(1):67–75. doi: 10.1006/taap.1998.8577. [DOI] [PubMed] [Google Scholar]
- Oguntoke O.A. Association of water-borne diseases morbidity pattern and water quality in parts of Ibadan City, Nigeria. Tanzan. J. Health Res. 2009;11(4):189–195. doi: 10.4314/thrb.v11i4.50174. [DOI] [PubMed] [Google Scholar]
- Pandey S. Water pollution and health. Kathmandu Univ. Med. J. 2006;4(1):128–134. [PubMed] [Google Scholar]
- Parveen S.A. Microbial Contamination of water in around Dhaka city. Bangladesh J. Sci. Ind. Res. 2008;43(2):273–276. [Google Scholar]
- Parvez A.K. Bacteriological quality of drinking water samples across Bangladesh. Arch. Clin. Microbiol. 2016;7(1):9. [Google Scholar]
- Patra R.W., Azadi M.A. Hydrological conditions influencing the spawning of major carps in the Halda river, Chittagong, Bangladesh. Bangladesh J. Zool. 1985;13(1):63–72. [Google Scholar]
- Prasad A.S. Federation Proceedings. 1984. Discovery and importance of zinc in human nutrition; pp. 2829–2834. [PubMed] [Google Scholar]
- Puri A., Kumar M. A review of permissible limits of drinking water. Indian J. Occup. Environ. Med. 2012;16(1):40. doi: 10.4103/0019-5278.99696. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Quintero-Gutiérrez A.G., González-Rosendo G., Sánchez-Muñoz J., Polo-Pozo J., Rodríguez-Jerez J.J. Bioavailability of heme iron in biscuit filling using piglets as an animal model for humans. Int. J. Biol. Sci. 2008;4(1):58–62. doi: 10.7150/ijbs.4.58. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Rabbi F., Uddin Z., Ahmed M., Majed N. Proceedings of 3rd International Conference on Advances in Civil Engineering. 2016. Pollution status of turag river: spatial and temporal variation of water quality; pp. 31–36. Chittagong. [Google Scholar]
- Rahman M.A., Bakri D.A. A study on selected water quality parameters along the river Buriganga, Bangladesh. Iran. J. Energy Environ. 2010;1(2):81–92. [Google Scholar]
- Rahman K.M., Debnath S.C. Agrochemical use, environmental and health hazards in Bangladesh. Int. Res. J. Interdiscip. Multidiscip. Stud. 2015;1(6):75–79. [Google Scholar]
- Rahman M.A., Majumder R.K., Rahman S.H., Halim M.A. Sources of deep groundwater salinity in the southwestern zone of Bangladesh. Environ. Earth Sci. 2011;63(2):363–373. [Google Scholar]
- Rahman M.H. Risk assessment of pesticides used in Bangladesh. J. Civ. Eng. 1997;25(1):97–106. [Google Scholar]
- Rahman M.M. National Workshop on Conventional and Nuclear Technique for Pesticide Residues Studies in Food and Environment at IFRB. 2000. Pestcides: their uses and problems in context of Bangladesh. [Google Scholar]
- Rahman M.S., Saha N., Molla A.H. Potential ecological risk assessment of heavy metal contamination in sediment and water body around Dhaka export processing zone, Bangladesh. Environ. Earth Sci. 2014;71(5):2293–2308. [Google Scholar]
- Rahman M., Malek M., Matin M. Trend of pesticide usage in Bangladesh. Sci. Total Environ. 1995;159(1):33–39. [Google Scholar]
- Rahman S.H. IAHS publication; 2009. Investigation of Shallow Tube-Well Water Quality Considering the Influence of Nearby Latrines in a Rural Village of Bangladesh; pp. 299–304. [Google Scholar]
- Rahman S.H. Water quality of shallow tube wells as affected by sanitary latrines and groundwater flow. J. Bangladesh Acad. Sci. 2013;37(2):231–243. [Google Scholar]
- Rahman S.R. Cypermethrin residue analysis of fruit and soil samples in eggplant ecosystem in Bangladesh. Sci. Lett. 2015;3(3):138–141. [Google Scholar]
- Rahman S., Hossain F. Spatial assessment of water quality in peripheral rivers of Dhaka city for optimal relocation of water intake point. Water Resour. Manag. 2008;22(3):377–391. [Google Scholar]
- Rahman S., Khan M.T., Akib S., Biswas S.K. Investigation of heavy metal pollution in peripheral river water. Pensee J. 2013;75(10):421–435. [Google Scholar]
- Rana A.K. brac; Dhaka: 2009. Effect of Water, Sanitation and hygiene Intervention in Reducing Self-Reported Waterborne Diseases in Rural Bangladesh. [Google Scholar]
- Rashid H., Hasan M.N., Tanu M.B., Parveen R., Sukhan Z.P., Rahman M.S., Mahmud Y. Heavy metal pollution and chemical profile of Khiru river, Bangladesh. Int. J. Environ. 2012;2(1):57–63. [Google Scholar]
- Rasul M.G., Faisal I., Khan M.M. Environmental pollution generated from process. Int. J. Environ. Pollut. 2006;28(1-2):144. [Google Scholar]
- Rasul M.T. Quality of ground and surface water of Rajshahi city area for sustainable drinking water source. J. Sci. Res. 2010;2(3):577–584. [Google Scholar]
- Rauh V.A. Impact of prenatal chlorpyrifos exposure on neurodevelopment in the first 3 years of life among inner-city children. Pediatrics. 2006;118(6):1845–1859. doi: 10.1542/peds.2006-0338. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Rauh V.A., Garfinkel R., Perera F.P., Andrews H.F., Hoepner L., Barr D.B. Impact of prenatal chlorpyrifos exposure on neurodevelopment in the first 3 Years of life among inner-city children. Pediatrics. 2006;118(6):1845–1859. doi: 10.1542/peds.2006-0338. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Ravenscroft P. 2011. Arsenic Pollution of Groundwater in Bangladesh; pp. 181–192. [Google Scholar]
- Reddy C.S., Pasha S.V., Jha C., Diwakar P., Dadhwal V. Development of national database on long-term deforestation (1930–2014) in Bangladesh. Glob. Planet. Chang. 2016;139:173–182. [Google Scholar]
- Richey A.S., Thomas B.F., Lo M.-H., Reager J.T., Famiglietti J.S., Voss K. Quantifying renewable groundwater stress with GRACE. Water Resour. Res. 2015;51:5217–5238. doi: 10.1002/2015WR017349. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Roy P. 2017, July 17. Tannery Relocation Impact: Situation Getting Better, Slowly.http://www.thedailystar.net/frontpage/dhaka-tannery-relocation-impact-situation-getting-better-slowly-1434166 Retrieved from The Daily Star: [Google Scholar]
- Roy P., Karmakar K. 2015, 6 27. Pesticide in Litchi Kills Kids, Again.http://www.thedailystar.net/frontpage/pesticide-litchi-kills-kids-again-103651 Retrieved 2 3, 2018, from. [Google Scholar]
- Sabrina M.U. Analysis of WASA supplied drinking water around Dhaka city from laboratory analysis perspective. Int. J. Chem. Phys. Sci. 2013;2:20–27. [Google Scholar]
- Saha M.L., Khan M.R., Ali M., Hoque S. Bacterial load and chemical pollution level of the River Buriganga, Dhaka, Bangladesh. Bangladesh J. Bot. 2009;38(1):87–91. [Google Scholar]
- Saha P.K. 2nd International Conference on Environmental Science and Technology. IPCBEE; Singapore: 2011. Assessment of heavy metal contamination and sediment quality in the Buriganga River, Bangladesh; pp. 26–28. [Google Scholar]
- Sandstead H.H. Zinc interference with copper metabolism. JAMA J. Am. Med. Assoc. 1978;240(20):2188. doi: 10.1001/jama.1978.03290200066029. [DOI] [PubMed] [Google Scholar]
- Sauders B.D., Overdevest J., Fortes E., Windham K., Schukken Y., Lembo A., Wiedmann M. Diversity of Listeria species in urban and natural environments. Appl. Environ. Microbiol. 2012;78(12):4420–4433. doi: 10.1128/AEM.00282-12. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Seddique A.A., Masuda H., Hoque A. Radionuclide and heavy metal contamination in the paleobeach groundwater, Cox’s Bazar, Bangladesh: potential impact on environmen. Arab. J. Geosci. 2016;9(7):488. [Google Scholar]
- Shammi M., Rahman R., Rahman M.M., Moniruzzaman M., Bodrud-Doza M., Karmakar B., Uddin M.K. Assessment of salinity hazard in existing water resources for irrigation and potentiality of conjunctive uses: a case report from Gopalganj District, Bangladesh. Sustain. Water Res. Manag. 2016;2(4):369–378. [Google Scholar]
- Shar A.H., Kazi Y.F., Zardari M., Soomro I.H. Enumeration of total and faecal coliform bacteria in drinking water of Khairpur city. Bangladesh J. Microbiol. 2007;24(2):163–165. [Google Scholar]
- Shiekh M.A. High degree of fecal contamination in river, lake and pond waters in⁄ and around Dhaka city of Bangladesh. Pak. J. Biol. Sci. 2006;9(1):141–144. [Google Scholar]
- Shiklomanov I. World fresh water resources. In: Gleick P.H., editor. Water in Crisis: A Guide to the World's Fresh Water Resources. Oxford University Press; New York: 1993. [Google Scholar]
- Shoeb M.M. Organochlorine pesticide residues in poultry meats of Bangladesh. Croat. J. Food Sci. Technol. 2016;8(1):30–33. [Google Scholar]
- Shoeb M.N. Nitrofuran antibiotics and organochlorine pesticides in Fish and Poultry Fish, Feed ingredients, and water samples collected from shrimp cultivation area. J. Bangladesh Chem. Soc. 2009;22(1):1–8. [Google Scholar]
- Shrivastava R., Upreti R., Seth P., Chaturvedi U. Effects of chromium on the immune system. FEMS Immunol. Med. Microbiol. 2002;34(1):1–7. doi: 10.1111/j.1574-695X.2002.tb00596.x. [DOI] [PubMed] [Google Scholar]
- Sikder M.T., Kihara Y., Yasuda M., Yustiawati, Mihara Y., Tanaka S. river water pollution in developed and developing countries: judge and assessment of physicochemical characteristics and selected dissolved metal concentration. Clean. Soil, Air, Water. 2013;41(1):60–68. [Google Scholar]
- Smith A.H., Lingas E.O., Rahman M. Contamination of drinking-water by arsenic in Bangladesh: a public health emergency. Bull. World Health Organ. 2000;78(9):1093–1103. [PMC free article] [PubMed] [Google Scholar]
- Soja R., Wiejaczka Ł. The impact of a reservoir on the physicochemical properties of water in a mountain river. Water Environ. J. 2014;28(4):473–482. [Google Scholar]
- Statistics B.B. Bangladesh Bureau of Statistics; Dhaka: 2009. Bangladesh National Drinking Water Quality Survey. [Google Scholar]
- Subramanian Water quality in south Asia. Asian J. Water Environ. Pollut. 2004;1(1-2):41–54. [Google Scholar]
- Sujauddin M., Huda S.M., Hoque A.R. Household solid waste characteristics and management in Chittagong, Bangladesh. Waste Manag. 2008;28(9):1688–1695. doi: 10.1016/j.wasman.2007.06.013. [DOI] [PubMed] [Google Scholar]
- Sultana M.S., Islam M.S., Saha R., Al-Mansur M. Impact of the effluents of textile dyeing industries on the surface water quality inside D.N.D embankment, Narayanganj. Bangladesh J. Sci. Ind. Res. (India) 2009;44(1):65–80. [Google Scholar]
- Sun Y., Fang Q., Dong J., Cheng X., Xu J. Removal of fluoride from drinking water by natural stilbite zeolite modified with Fe(III) Desalination. 2011;277(1-3):121–127. [Google Scholar]
- Swaminathan S., Fonseca V.A., Alam M.G., Shah S.V. The role of iron in diabetes and its complications. Diabetes Care. 2007;30(7):1926–1933. doi: 10.2337/dc06-2625. [DOI] [PubMed] [Google Scholar]
- Talukdar P.K. Antimicrobial resistance, virulence factors and genetic diversity of Escherichia coli isolates from household water supply in Dhaka, Bangladesh. PLoS One. 2013;8(4) doi: 10.1371/journal.pone.0061090. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Tandouan B., Ulusu N.N. Importance of calcium. Turk. J. Med. Sci. 2005;35:197–201. [Google Scholar]
- Tilzer M.M. Dept. of Botany, Dhaka University; 1993. Hypertrophic and Polluted Freshwater Ecosystems: Ecological Basis for Water Resource Management. [Google Scholar]
- Todar K. 2007. Pathogenic E. coli. Online textbook of bacteriology. [Google Scholar]
- Toyokuni S. Role of iron in carcinogenesis: cancer as a ferrotoxic disease. Cancer Sci. 2009;100(1):9–16. doi: 10.1111/j.1349-7006.2008.01001.x. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Türkdoğan M., Kilicel F., Kara K., Tuncer I., Uygan I. Heavy metals in soil, vegetables and fruits in the endemic upper gastrointestinal cancer region of Turkey. Environ. Toxicol. Pharmacol. 2002;13(3):175–179. doi: 10.1016/S1382-6689(02)00156-4. [DOI] [PubMed] [Google Scholar]
- Uddin M.A. Pesticide residues in some selected pond water samples of Bangladesh. Bangladesh J. Sci. Res. 2012;25(1):93–97. [Google Scholar]
- Uddin M.A. Pesticide residues in some selected pond water samples of Meherpur region of Bangladesh. J. Asiat. Soc. Bangladesh (Sci.) 2013;39(1):77–82. [Google Scholar]
- UNEP . United Natons Environment Programme; 2016. A Snapshot of the World’s Water Quality: towards a Global Assessment.https://uneplive.unep.org/media/docs/assessments/unep_wwqa_report_web.pdf Retrieved from. [Google Scholar]
- UNESCO . UNESCO Publishing Group; Paris: 2009. The United Nations World Water Development Report 3 Water in a Changing World. [Google Scholar]
- UN-Water . UN-Water; 2001. Water Quality. [Google Scholar]
- UN-Water . 2013, May 8. UN-water Country Briefs Bangladesh.http://www.unwater.org/publications/un-water-country-briefs-zambia/# Retrieved from UN Water: [Google Scholar]
- Uttam K., Chowdhury B.K. Groundwater arsenic contamination in Bangladesh and West Bengal, India. Environ. Health Perspect. 2000;108(5):393–397. doi: 10.1289/ehp.00108393. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Vallee B.L., Wacker W.E., Ulmer D.D. The magnesium-deficiency tetany syndrome in man. Boston Med. Surg. J. 1960;262(4):155–161. doi: 10.1056/NEJM196001282620401. [DOI] [PubMed] [Google Scholar]
- van Geen A., Ahmed K.M., Akita Y., Alam M.J., Culligan P.J., Emch M. Fecal contamination of shallow tubewells in Bangladesh inversely related to arsenic. Environ. Sci. Technol. 2011;45(4):1199–1205. doi: 10.1021/es103192b. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Whelton A., Dietrich A., Burlingame G., Schechs M., Duncan S. Minerals in drinking water: impacts on taste and importance to consumer health. Water Sci. Technol. 2007;55(5):283. doi: 10.2166/wst.2007.190. [DOI] [PubMed] [Google Scholar]
- WHO . World Health Organization; 2004. Guidelines for Drinking-Water Quality. [Google Scholar]
- WHO . World Health Organization; Geneva: 2008. Guidelines for Drinking Water Quality. [Google Scholar]
- WHO . fourth ed. World Health Organization; 2011. Guidelines for Drinking-Water Quality. [Google Scholar]
- WHO . 2016. WHO and Maternal and Child Epidemiology Estimation Group (MCEE) Estimates 2015.http://apps.who.int/gho/data/node.main.ChildMort?lang=en Geneva. Retrieved 2 2, 2018, from. [Google Scholar]
- WHO . 2017, July. Drinking-water Fact Sheets.http://www.who.int/mediacentre/factsheets/fs391/en/ Retrieved from World Health Organization: [Google Scholar]
- WHO . World Health Organization; Geneva: 2017. UN-water Global Analysis and Assessment of Sanitation and Drinking-Water (GLAAS) 2017 Report: Financing Universal Water, Sanitation and hygiene under the Sustainable.www.who.int/water_sanitation_health/publications/glaas-report-2017/en/ Retrieved from. [Google Scholar]
- WHO . 2018, February 5. Sustainable Development & Healthy Environment.http://www.whoban.org/sust_dev_mental_env.html Retrieved from WHO Bangladesh: [Google Scholar]
- Winton E.F., Tardiff R.G., McCabe L.J. Nitrate in drinking water. Am. Water Works Assoc. 1971;63(2):95–98. [Google Scholar]
- WWAP . UNESCO; Paris: 2012. The United Nations World Water Development Report 4: Managing Water under Uncertainty and Risk. [Google Scholar]
- Yokota H., Tanabe K., Sezaki M., Akiyoshi Y., Miyata T., Kawahara K. Arsenic contamination of ground and pond water and water purification system using pond water in Bangladesh. Eng. Geol. 2001;60:323–331. [Google Scholar]
- Yunus M., Sohel N., Hore S.K., Rahman M. Arsenic exposure and adverse health effects: a review of recent findings from arsenic and health studies in Matlab, Bangladesh. Kaohsiung J. Med. Sci. 2011;27(9):371–376. doi: 10.1016/j.kjms.2011.05.012. [DOI] [PubMed] [Google Scholar]
- Zahid A., Hassan M.Q., Balke K.-D., Flegr M., Clark D.W. Groundwater chemistry and occurrence of arsenic in the Meghna floodplain aquifer, southeastern Bangladesh. Environ. Geol. 2008;54(6):1247–1260. [Google Scholar]
- Zakir H.M., Rahman M.M., Rahman A., Ahmed I., Hossain M.A. Heavy metals and major ionic pollution assessment in waters of midstream of the river Karatoa in Bangladesh. J. Environ. Sci. Nat. Res. 2012;5(2):149–160. [Google Scholar]
- Zhang L., Wan L., Chang N., Liu J., Duan C., Zhou Q. Removal of phosphate from water by activated carbon fiber loaded with lanthanum oxide. J. Hazard Mater. 2011;190(1-3):848–855. doi: 10.1016/j.jhazmat.2011.04.021. [DOI] [PubMed] [Google Scholar]
- Zuane J.D. second ed. John Wiley & Sons; New York: 1996. Handbook of Drinking Water Quality. [Google Scholar]
- Zuthi M.F. Assessment of supply water quality in the Chittagong city of Bangladesh. ARPN J. Eng. Appl. Sci. 2009;4(3):73–80. [Google Scholar]