American-Eurasian J. Agric. & Environ. Sci., 21 (3): 151-167, 2021
ISSN 1818-6769
© IDOSI Publications, 2021
DOI: 10.5829/idosi.aejaes.2021.151.167
Trends of Chemical Pesticide Consumption and its Contamination Feature of
Natural Waters in Especial Reference to Bangladesh: A Review
Md. Shajedul Islam and M.G. Mostafa
Institute of Environmental Science, University of Rajshahi, Rajshahi 6205, Bangladesh
Abstract: Collection of chemicals that can resist pests and diseases, pesticides are now an extensively used
tool for pest and disease managing across agrarian countries like Bangladesh. In the country, pesticide use
grew at an alarming rate of 10% per annum, while the corresponding response in production growth of main
crops has been negligible (<1% y 1). Globally, 750% increase in pesticides production from 1955 to 2000 and
that period minimum 30 countries have highly contaminated by these hazardous substances. Bangladesh lies
in the second position on the list of fast-growing pesticide-consuming countries in the world. The review paper
focused on the present pesticide consumption rate in the country and entire world, their environmental fate and
how much contaminate the natural water resources through the application of chemical pesticides. For this
purpose, we reviewed over 50 related literatures to extract expressive info about the national wide water
contamination by pesticides and presented methodically. Results show that among the Organophosphorus and
Carbamate pesticides such as Chlorpyrifos, Diazinon, Malathion, Parathion, Carbaryls, Carbofuran and
Cypermethrin was identified in various surfaces and groundwater samples and maximum of those are above the
World Health Organization (WHO) guideline value. The serious concern is that in many regions of Bangladesh,
organochlorine insecticides such as Dichlorodiphenyldichloroethane (DDD), Dichlorodiphenyldichloroethane
(DDE), Dichlorodiphenyltrichloroethane (DDT), Aldrin and Dieldrin was found in the range of 0.01 to 1.20 mg/L
which are much higher than recognized level. To control the misapplication of pesticides and to reduce the
possible environmental risk, appropriate regulatory systems of pests such as the Integrated Pest Management
(IPM) system and the use of bio- or herbal pesticides should be applied immediately in the country.
Key words: Bangladesh
Chemical Pesticides
Global Pesticide Consumption
Management (IPM) Water Contamination
Integrated Pest
those noxious substances with other organic pollutants
in agricultural sectors of vast farming areas may damage
the soils and water environment due to their persistent
and ubiquitous nature [4].
Bangladesh is a densely peopled (2890/mile2, which
ranks 10th in the world) and a vast agrarian country.
Nearly 90% of its lands are cultivatable and 55% of the
residents are involved in the farming sector [5]. This
sector plays a vital role in the country's economy, which
accounts for about 21% of participation in the national
gross domestic product (GDP) [5]. There is an estimate of
70, 000 different pest varieties together with plant
pathogens, insects and mites and weeds which cause an
estimated 13, 14 and 13% farming crop damage,
respectively in the world [6]. But 5500 registered varieties
of pesticides are used in Bangladesh [7]. In the country
INTRODUCTION
Chemical pesticides are working in several
agricultural activities to control pests, unwanted plants
and diseases in crops. Insecticides, fungicides,
herbicides, nematicides, rodenticides, etc., are the major
class of pesticides. Those are vital tools for crop
protection and better yield in the agricultural process.
Almost, 50% of the yearly food production is lost owing
to pest attacks in the vast agrarian countries. So, actual
pest management by using extensive categories of
pesticides is obligatory to encounter pests and to
increase the yield [1]. Though, from the mid-nineteen
century, about 750% increases in production of chemical
pesticides globally but these often persuade calamitous
impacts on the natural environment [2, 3]. Improper use of
Corresponding Authors: M.S. Islam & M.G. Mostafa, Institute of Environmental Science, University of Rajshahi,
Rajshahi 6205, Bangladesh. E-mail: shajedulkst@gmail.com, mgmostafa@ru.ac.bd.
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around 40% of the crop loss is caused by insects and
pests attacks which are a significant loss [8]. Peshin and
Dhawan [6] stated that crop loss from pests can reduce to
35-42% using pesticides, even though the hazards of
using pesticides are serious as well. Owing to insufficient
knowledge and guidance about the uses of pesticides,
growers spray extreme amounts of pesticides in the
farming lands in Bangladesh [9, 10].
The natural water bodies are easily polluted by runoff
water or by rain-wash for the undiscerning use of
pesticides. The extensive use of pesticides may pollute
the environment and freshwater biota [11, 12]. It is
compulsory to incoming the portions of applied
insecticides and pesticides into the aquatic ecosystems
because of the unscientific application techniques for
crop protection [13-15]. In this study, we reviewed
numerous published literature and briefly described and
established the present situation of countrywide water
contamination by residual pesticides. In addition, we have
discussed the global trend of pesticides consumption and
the rate of water contamination by them.
Jepson et al. [16] classified a total of 659 chemical
pesticides based on their hazard to human well-being and
the ecosystem. The pesticide residues from water bodies
directly or indirectly pass through the food wave and
ultimately harm human and terrestrial or other aquatic
lives. Numerous problems can cause in the human
physique
because
of
pesticide
exposure.
Organophosphorus pesticides may affect sperm
chromosome segregation and supplement the risk for
genomic syndrome [17, 18]. Lee et al. [19] described a
connotation between chlorpyrifos use and the occurrence
of lung cancer in North Carolina and Iowa (USA) and the
connotation of soft-tissue sarcoma with definite
pesticides such as Diazinon and Aldrin in 6 regions of
Canada has been observed [20]. Organochlorine (OC)
pesticides such as Dichlorodiphenyldichloroethane
(DDD),
Dichlorodiphenyldichloroethane
(DDE),
Dichlorodiphenyltrichloroethane (DDT), Aldrin, Dieldrin,
etc. use are related to an increase in cancer risk [21-23].
A very few studies about the health impacted by residual
pesticides have been conducted in Bangladesh. Endrin
was the first introduced pesticide in Bangladesh of which
3 metric tons (MT) were imported in 1955 for farming pest
control [24]. Initially, the Bangladesh government
providing 100% financial support for pesticides and
provided free of cost to the farmers but the pesticide
industry has gone to farmers in 1979 when the 100% price
was obligatory [25]. In this country, from 1995 to 2019,
the consumption of chemical pesticides is increased by
500% [26]. A portion of this huge amount of applied
pesticides remains in the environment and on a long-term
basis, this residue can cause serious toxicity in nature.
Water is the final receiver of pesticides and it can vastly
contaminate these substances. This study is envisioned
to deliver a general understanding of pesticide use in
developing countries with Bangladesh, including the
scale of the consumption, most distinguished trends,
including the environmental impacts and the role they
play concerning water quality.
Pesticides Consumption in Bangladesh: In Bangladesh,
farmers widely use chemical pesticides (Table 1) rather
than bio- or natural pesticides for pest control of their
reputation for quick effectiveness. Though, the rising use
of chemicals has already posed a serious health risk as
well as threatening extensive biodiversity and ecological
harms. In the country, some illegal traders are engaging
themselves in selling some banned items by violating the
Government Ordinance (Ordinance No. II of 1971),
modified in 1984 which makes foolish to the illiterate
farmers [10]. These issues eventually increase the cost of
crop production and leading pesticide contamination
alarmingly in the country. In addition, some reports have
revealed that most of the farmers are not aware of the
minimum safety measure of pesticides. Nowadays, the
good news is some Government and Non-governmental
Organizations (NGO’s) are trying to motivate farmers to
increase their awareness about pesticide safety measures.
In Bangladesh, just 8000 metric tons (MT) of
chemical pesticides were used in 1997, but this amount
reaches approximately 40, 000 MT in 2018, i.e.,
consumption is increasing by 500% (Figure 1). The survey
of Pretty and Bharucha [26] indicated that Bangladesh lies
in the second position on the list of fast-growing
pesticide-consuming countries (Figure 1). The total
registered pesticides are 5500 and 90% of the consumed
pesticides were imported from China, the rest from India,
Germany and other countries. But pesticide use drops
25% in the last 7 years (Global Plant Protection News,
November 2016). The use of chemical pesticides is
gradually decreasing (Figure 2) due to Integrated Pest
Management (IPM) practices and promotion against the
use of chemical pesticides. It gives a great scope of use of
Bio-pesticides in Bangladesh. The variety of pest control
substances that are widely used in Bangladesh are listed
in Table 1. The used pesticides in Bangladesh are
moderate to highly toxic to every biota and according to
WHO, all of them are category I and II hazardous material
(Table 1). The common health effects of those pests are
dizziness, excessive sweating, fatigue, nausea/vomiting,
dizziness, cough; and diarrhea for the human body.
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Table 1: Types of chemical pesticides used in Bangladesh and relative health impacts
Pesticides
Chemical type
Hazard characteristics
Edifenphos
Organophosphate
Highly toxic
Carbofuran
Carbamate
Highly toxic
Monocrotophos
Organophosphate
Highly toxic
DDT, DDE, DDD
Organo-chlorine
Highly toxic
Cyhalothrin
Pyrethroid
Moderately toxic
Diazinon
Organophosphate
Moderately toxic
Cypermethrin
Pyrethroid
Moderately toxic
Chlorpyrifos
Organophosphate
Moderately toxic
Malathion
Dioxathion
Organophosphate
Organophosphate
Slightly toxic
Not classified
Fig. 1:
Health effect
excessive sweating; dizziness; fatigue, nausea/vomiting;
dizziness; cough; diarrhea
cough; diarrhea excessive sweating; dizziness; fatigue,
nausea/vomiting; dizziness
dizziness; excessive sweating; fatigue, diarrhea. nausea;
vomiting; dizziness; cough
excessive sweating; dizziness; fatigue, nausea/vomiting;
dizziness; cough; diarrhea
burning nose; skin redness/white patches on skin/ skin
scaling; burning/stinging/itching eyes
nausea; vomiting; excessive sweating; dizziness; fatigue,
dizziness; cough; diarrhea.
excessive sweating; dizziness; fatigue, nausea/vomiting;
dizziness; cough; diarrhea
dizziness; excessive sweating; fatigue, nausea/vomiting;
dizziness; cough; diarrhea
burning nose; headache
----
WHO categorized class
Class Ib
Class Ib
Class Ib
Class Ib
Class II
Class II
Class II
Class II
Class III
----
Pesticide consumption rate from 1990 to 2012 in Bangladesh comparing other countries Only showing countries
that use over 20 million kg of pesticides annually (source: Pretty and Bharucha, [26])
Fig. 2: The rate of chemical pesticide consumption in Bangladesh (2006-2018)
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Fig. 3: Category wise chemical pesticide use in the agricultural field of Bangladesh
The arrangement of pesticides over time was
conquered by the fungicides and insecticides ranging
from 75% to 97% (mean 84%) of total pesticide use
(Figure 3). Fungicides got a peak of 29% of total pesticide
use only in 1981 and compressed dramatically afterward
[27]. Nevertheless, the use of herbicides and fungicides
has been increasing gradually in recent past years.
At present fungicide and herbicides uses 45% and 16% of
total consumption respectively. The main reasons for the
increased use of granular insecticides and fungicides are
a lengthier protection period, confirmed effectiveness,
the lack of effective spray kits and a ‘ready to use’ design
[28]. While statistics do not exist in the configuration of
chemical pesticides, data for the year 1987/88 is available
and this data showed that Organophosphates are the
major types (60.2%) after that Carbamates (28.8%),
Organochlorines (7.5%) and others (3.5%) [29]. The farmlevel indication also delivers a comparable picture.
For instance, Rahman [30] stated that 69.3% of the 410
surveyed agriculture growers used Organophosphates
after that Carbamates (19.1%), Organochlorines (6.6%)
and Pyrethroids (4.6%).
Pesticide production is decreasing steadily at a rate
of -8.6% per annum in Bangladesh [30]. Implementation
of Green Revolution Technology (GRT), crops
divergence, farmland size and awareness rate is the
substantial determinants of pesticide use. Even though
the government has shifted focus from pesticide use to
integrated pest management (IPM), its coverage remains
insufficient as only 7.4% of the total farmers are covered
after 30 years of effort [10]. Development of IPM through
public and constricted pesticide regulation and its active
execution, private and NGO stakeholders are suggested to
decrease pesticide consumption.
Pesticide Consumption – Global Scale: At present, the
total cultivable land area is around 5 billion hectares or
38% of the global land surface [31]. A meta-study on
pesticide uses, a class of chemical products that have
seen a 750% increase in production from 1955 to2000,
things to see for the first time that natural water (the final
receiver of pesticides residue) may be at high risk from
pesticides exposure on a universal scale [2]. Stehle &
Schulz [32] were analyzed 838 published papers on
pesticides consumption and contamination from more
than 2500 places in 73 countries. The 28 chemical
pesticideswere designated because the majority is
permitted for application in the USA and the EU and they
cover all major pesticides categories: organochlorines,
carbamates,
pyrethroids,
organophosphorus
and
neonicotinoids. The study illustrations that 40% of the
pesticides concentrations measured in natural waters
and 80% of the pesticides levels measured in soils
and sediments exceed monitoring threshold limits and
result in declining aquatic biodiversity and ecosystems.
In addition, they were found there is no scientific
investigation or monitoring of pesticide pollution for 90%
of the global farmland. The lack of monitoring appears
mostly severe in crops-rich countries like China, South
American, South Asia and some areas of Africa.
Generalizing results from checked to unchecked waters,
the scientists estimate that 65% of global cultivated zones
are at high risk for exposure to pesticides [2]. A statistical
investigation reveals that concentrations are mostly high
for a newer group of pesticides like pyrethroids, a class of
prevalent domestic insecticides [33, 34].
Now a day, less developed countries are in great
vulnerable to pesticide contamination in the local
environment. Pesticides are extensively used all over the
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Fig. 4: The scale of pesticide uses in selected developing countries
developing world and their demand is rising due to the
recent crop yield system, which prioritizes high
agricultural productions. Nonetheless, government grants
for pesticides have become less common in maximum
developing countries in the later 1990s, because of a
combination of structural adjustment policies and
emergent sustainability thoughtful. Presently, around 2
million tons of pesticides are consumed in less developed
countries per year [27]. This statistic will be increased in
the future particularly in the developing agrarian
countries. For example, in Brazil, prediction shows that
agricultural production will continue increasing and so
will the demand for pesticides. In the same country,
growth in 2020 relative to 2019 was projected at 6.6% in
terms of pesticide amount (9.75 million tons), 5.8% in
terms of national income; and 8.0% in terms of application
zone (1.6 billion hectares), of which 2% denoted to new
agrarian areas [34].On the other hand, 47% increase in
pesticide use from 2015 to 2019 in Ukraine and this trend
is expected to continue [35]. The complete scenarios of
pesticide use in farmland (kg/hectare) and the amounts
imports per year of the developing countries in the world
are showed by mapping as Figure 4. Globally, entire South
American regions, China, South Asia with Indonesia and
Thailand, Iran and western-southern countries of Africa
are in the top position concerning pesticide consumption
and import [36]. Sharma’s study [27] and EU report [34]
given similar statistics of FAO. These reports are good for
more yields but it brings us serious ecological impacts
which damage public health and more loss of biodiversity.
The ultimate and final receiver of the pesticide’s residue
after use is the natural surface water as well as
groundwater through effective leaching. If the abovementioned global trends of increasing pesticide
consumption continue, thus indicating more and more
water-body contamination.
Environmental Fates of Pesticides: All traditional
pesticides do have not equal toxic impacts on the
environment. Jepson et al. [16] classified a total of 659
chemical pesticides based on their hazard to human
well-being and the ecosystem. Among them, 243 classes
have a lower risk to biota and farmers need to use
single-layer personal protection equipment (PPE) in
applying time. On the other hand, 95 are lesser hazardous
(additional PPE mandatory) and 163 have a high risk to the
human body. Besides, 158 types of pesticides are
obsolete materials and highly hazardous; those handles
with maximum consciously. It is well known that chemical
pesticides for agricultural purposes have created more or
less human health and environmental impacts.
Nevertheless, the statistics remain largely unimaginable.
It is projected that 1 to 5 million agricultural employees are
affected by pesticide toxicity per year and the WHO
reports that a minimum of 20, 000 farmworkers dies from
exposure to pesticides every year in the world [37].
The use of lethal chemical pesticides in agriculture
activities not only generate different diseases in the
human body (over 200 diseases stated by WHO) such
as kidney diseases, cancer, skin diseases, affects the
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Fig. 5: The pathways of pesticide contamination in the environment
nervous system, hypertension, irritate skin and eye, etc.
but also contaminate the water, soil and air, through
surface run-off with leaching the residual portion [14].
Also, pesticides can affect others animals, birds, aquatic
lives, plants, as well as total ecosystem. The pathway of
pesticides contamination in the environment showed in
Fig. 5.
The main attention is the impact of chemical
pesticides on non-target species. Near about 100% of
sprayed herbicides and insecticides reach a terminus
other than their target species, because they spread or
sprayed across whole croplands [38]. Run-off can
transport pesticides into the water body and the wind can
transmit them to other fields or the human environment.
Additional problems arise from the poor production
systems and transport and storage performance [39].
Over time, the regular application intensifies pest
resistance, but its effects on other species can enable pest
resurrection [40].
Water bodies are the ultimate receiver of residual
pesticides. The impacts of pesticides on natural aquatic
systems are regularly studied using a hydrological
transportation model to study the transport and fate of
substances in rivers, streams, or fixed water bodies.
There are 4 key routes through which pesticides reach the
water: a) it may stream or drift externally the desired area
when it is sprayed, b) it may infiltrate, or leach into the
topsoil, c) it may be passed to the water body as runoff,
or/and d) it may be dropped, e.g., unintentionally or
through negligence [41]. Residual pesticides may also be
carried in water by soil corroding. Influences that affect a
pesticide's capability to pollute water included its water
solubility, the distance from an application spot to a
water body, soil type, weather, the presence of a growing
crop and the technique used to apply the pesticide [42].
The soil of Bangladesh is very coarse and sandy and that
is why the residual part of pesticides easily penetrates the
groundwater.
Pesticide Pollution in Bangladesh
Groundwater Contamination: Globally, ever collective
demand for food and agricultural resources has led to an
increase in pesticide toxicity and environmental threat
[43]. Agriculture is the determining factor of the
Bangladesh economy. Nationally, around 7 kg of 5500
varieties of chemical pesticides are consumed per hectare
[36] and annually 37, 258 tons of pesticides are used in
total farmland [7]. Runoff of pesticides is a serious hazard
of Bangladesh, may leach into groundwater, causing
public health problems from polluted water wells [44].
Overall, more pesticide ingredients detected as
groundwater quality monitoring programs have become
more widespread, but much less monitoring conducted in
developing countries, like Bangladesh, because of high
investigation costs [44].
Pesticide poisoning of groundwater is an issue of
national consideration because groundwater is used for
potable purposes by about 95% of the nation's populace,
particularly in rural areas [45]. Before the mid-1970s, it was
thought that soil acted as a natural protective filter that
hindered pesticides from reaching unconfined
groundwater aquifers [46]. Nowadays, studies have
shown that this is not a fact. In Bangladesh, groundwater
tables are high and soil is mostly sandy, coarse and lose
types, so there is a big chance that groundwater can have
contaminated by the leaching of pesticide residues.
Anwar and Bari [47], Anwar and Saing [48] and Anwar
and Yunus [49] confirmed that the Leaching Potential
Index (LPI) of sediment and soil in the maximum zones of
Bangladesh is sufficiently high to leaching pesticides into
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Table 2: Pesticide contamination (mg/L) of groundwater samples in Bangladesh
Sampling location
Water type and depth
Pesticide detected
Concentration
WHO [45] Standard
Nayerhat, Dhaka District
STW 20-40 m
p.p'-Dichlorodiphenyldichloroethane, DDE Dieldrin
0 Traces
- 0.00003
Rahman [53]
Dhamrai upazila, Dhaka District
STW 25-40 m
Malathion Diazinon
0.0042 0.0003
0.0019 0.0020
Hasanuzzaman et al. [54]
Deferent region of Bangladesh
STW
Matin et al. [55]
Daudkandi, Comilla District
Ghior, Manikganj District
Nagarpur, Tangail District
STW 07
STW 21
STW 42
p.p'-Dichlorodiphenyldichloroethane, DDD
0.014-0.365
0.001
p.p'-Dichlorodiphenyldichloroethane, DDE
0.010-0.084
0.001
p.p'-Dichlorodiphenyltrichloroethane, DDT
0.027-1.204
0.001
Heptachlor
0.025-0.789
0.00003
p.p'- Dichlorodiphenyldichloroethane, DDD
BDL
0.001
p.p'- Dichlorodiphenyltrichloroethane, DDT
BDL
0.001
p.p'- Dichlorodiphenyldichloroethane, DDE
BDL
0.001
Malathion
BDL
-
Diazinon
BDL
-
Chlorpyrifos
BDL
0.03
Cypermethrin
BDL-310
-
Chlorpyrifos
BDL-34.6
0.03
Diazinon
BDL-27
-
Malathion
0.0258
-
Diazinon
0.0002
-
Chlorpyrifos
0.0037
0.03
p.p'- Dichlorodiphenyldichloroethane, DDD
BDL
0.001
p.p'- Dichlorodiphenyldichloroethane, DDE
BDL
0.001
p.p'- Dichlorodiphenyltrichloroethane, DDT
BDL
0.001
Ref.
Hasanuzzaman et al. [56]
Shubhra et al. [57]
Hasanuzzaman et al. [10]
BDL-Bellow detection limit
Fig. 5: Water contaminated area by pesticide in Bangladesh
the subsurface environment. Pesticides, like most other
chemical contaminants, can easily reach water-bearing
layers from cultivation fields, seepage of polluted surface
water, inappropriate disposal, unintentional or accidental
spills and leaks and even through injection waste
substances into wells [50].
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Accumulated pesticides can create a serious
long-term risk to human body systems. In Bangladesh, the
pesticide exposure level (0.018 mg kg 1 day 1) is much
higher than that of the permissible level (0.005 mg kg 1
day 1) [51]. Thus, there is a substantial risk of exposure
threats of pesticides to humans and other non-targeted
species in Bangladesh. Runoff, spillage, washing of
pesticide containers in pond water non-contributor
pesticide residues to surface and groundwater in the
country. A study showed that 0.0448 mg/L concentration
of DDT arrived pond from the adjacent paddy field
through water by rain wash [10]. Some pesticides have
denominated the maximum contaminant limit in potable
water set by the WHO and US-EPA but many have not.
Similarly, in drinking water, the consequence of combining
more than one pesticide might be different than the things
of each specific pesticide alone [51, 52]. This is another
situation where has no adequate systematic data to draw
dependable conclusions.
Limited information is being available concerning
pesticide contamination of groundwater in Bangladesh.
Like other less-developed countries, inadequate financial
grants and laboratory services are the key hindrances to
the obtainability of data in the country. The results of
separate studies detailing pesticide accumulation in
groundwater of Bangladesh and the relevant WHO
standard values are arranged in Table 2. Most of the
farmers used mainly chlorinated hydrocarbons,
organophosphates, chlorophenoxiacids and carbamate
pesticides in Bangladesh and a residual portion of those
pesticides can accumulate in living beings through the
food chain or drinking water [58]. Organochlorinated
pesticides like Heptachlor, Dieldrin, DDT, Lindane were
generally used in farmlands and control diseases like
malaria in Bangladesh from the early ‘50s [12]. In 1993,
Bangladesh’s government banned those pesticides, but
there were reports that they used up unlawfully [59, 60].
Organochlorine pesticide having high lipophilicity, lower
polarity, less aqueous solubility and a very stable half-life
make it a serious threat to public health and the
environment as it can bio-accumulate in the food wave
[59, 61-64]. On the other hand, organophosphorus
pesticides are inexpensive and efficiency is very good,
farmers are stimulated to use them. Nonetheless, these
pesticides are very injurious to farmer's health and those
are also carcinogenic and genotoxic [65]. As chlorpyrifos
can cause attention to insufficient hyperactivity disease
and development uncertainty, both in embryo and
children [65, 66]. On the other hand, carbamate especially
carbofuran pesticides cause main problems in the
reproductive system and it can cause blurred vision,
breathing, vomiting and nausea problems [67].
After applying the pesticides, rain washes the
residues to the adjacent water bodies and they become
polluted [68]. Matin et al. [55] have collected 144
groundwater samples from around the country and found
maximum of the samples carried 10 to 1000 times higher
concentrations of pesticide residue than WHO
recommendation values (Table 2). In this investigation, all
DDT values found ranging from 0.27 to 1.204 mg/L were
very much higher than guideline values. They also found
Heptachlor residues ranging from 0.025 to 0.789 mg/L.
Another researcher Islam, [69] collected 48 cultivated field
water samples from various zones in the country and
found groundwater samples from 10 sites contaminated
by DDT, lindane and heptachlor. In this investigation,
DDT was found at Bogra and Rajbari Districts; lindane
was found in Dhaka, Noakhali, Sylhet and Shariatpur
Districts; and heptachlor was found in Dhaka, Chittagong
and Magura Districts in which the highest level of DDT
residue was estimated in Bogra and it was 0.54 ppm.
On the other hand, in Dhamrai and Savar Upazila, among
the 27 well water samples, carbofuran and diazinon were
found from Savar at 198.7 mg/L and 0.9 mg/L respectively.
In Dhamrai Upazila malathion, carbaryl and carbofuran
were found at 105.2 mg/L, 14.1-18.1 mg/L and 105.8 mg/L
separately [70]. Hossain et al. [71] also conducted studies
in the same places and find out the level of the same
parameters. Chowdhury et al. [72] collected water samples
from paddy fields, lakes and well in Rangpur city and
found carbofuran levels from 0.949 to 1.671 mg/L,
chlorpyrifos ranging from 0.554 to 0.895 mg/L and carbaryl
was 0.195 mg/L in the lake water. Also, they found
carbofuran in 7 samples ranging from 0.934 to 3.395 mg/L,
chlorpyrifos in 7 samples ranging from 0.477 to 1.189 mg/L
and carbaryl in 2 samples at 0.055 and 0.163 mg/L in the
paddy-field water samples. Besides, Chowdhury et al. [72]
collected irrigated groundwater samples from 22 districts
in Bangladesh and they detected DDT residue in
Rajshahi, Feni and Chapai Nawabganj Districts. The
uppermost DDT level was 8.29 mg/L. Also, they found
both heptachlor and DDT residues in water samples from
Chhatak at Sunamganj district and observed Heptachlor
residues in Madaripur, Sunamganj and Natore districts
with a maximum concentration of 5.25 mg/L. Sumon et al.
[73] measure the residues of 10 most generally used
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Table 3: Pesticide contamination (mg/L) of surface water samples in Bangladesh
Sampling location
Water type
Detected pesticide
Concentration
WHO [77] Standard
Ref.
Different regions of Bangladesh
River and pond water
p, p'- Dichlorodiphenyldichloroethane, DDE
p, p'- Dichlorodiphenyldichloroethane, DDD
0.013–0.060
0.014–0.038
0.001
0.001
Matin et al. [55]
p, p'- Dichlorodiphenyltrichloroethane, DDT
0.015–0.068
0.001
Savar and Dhamrai Upazila
Surface and paddy field water
Malathion
Diazinon
BDL-105.2
BDL-0.9
0.0019
0.0020
Carbaryl
Carbofuran
BDL-18.1
BDL-198.7
0.001
-
Chlorpyrifos
BDL-1.189
0.03
Carbofuran
Carbaryl
BDL-3.395
BDL-0.163
0.001
Rangpur district
Meherpur district
Surface and lake water
Surface water
Diazinon
BDL-0.0775
0.002
Chlorpyriphos
Carbofuran
BDL-0.0143
BDL-0.0387
0.03
-
Chowdhury [70]
Chowdhury [72]
Uddin et al. [74]
Carbaryl
BDL
0.001
Jessore district
Surface water
Quinalphos
BDL-0.241
-
Fatema et al. [75]
Savar Upazila
Surface and paddy field water
Cypermethrin
Chlorpyrifos
BDL-80.5
BDL-9.31
0.03
0.002
Hossain et al. [71]
Diazinon
Ethion
BDL-7.86
BD -56.3
-
Fenitrothion
Malathion
BDL-33.41
BDL-59.9
0.0042
-
Parathion
Carbofuran
BDL-6.23
BDL-43.2
0.001
-
Different spots in Bangladesh
48 different zones in Bangladesh
Comilla
Different regions of Bangladesh
River and pond water
Surface water
Surface water
Pond water
Carbaryls
BDL-6.3
-
p, p’-Dichlorodiphenyldichloroethane, DDD
p.p’-Dichlorodiphenyldichloroethane, DDE
BDL – 8.29
BDL-4.06
0.001
0.001
p, p’-Dichlorodiphenyltrichloroethane, DDT
Endrin
BDL
BDL
0.001
-
Lindane
Heptachlor
BDL
BDL-5.24
-
p, p’-dichlorodiphenyltrichloroethane Heptachlor
BDL-0.5401
0.001
Lindane
BDL-1.479
BDL-1.826
-
p.p’-Dichlorodiphenyldichloroethane, DDE
0.0001
0.001
Dieldrin
p, p’-Dichlorodiphenyltrichloroethane, DDT
0
6×10
0.001
p, p’-Dichlorodiphenyldichloroethane, DDD
BDL-0.052
0.001
p.p’-Dichlorodiphenyldichloroethane, DDE
p, p’-Dichlorodiphenyltrichloroethane, DDT
BDL-0.014
BDL-0.316
0.001
0.001
Heptachlor
Carbaryl
BDL-0.048
BDL-0.609
-
Carbofuran
BDL-1.760
-
6
Chowdhury et al. [72]
Islam [69]
Rahman [53]
Bagchi et al. [8]
BDL-Bellow detection limit
Organophosphorus pesticides, OPPs in water and
sediment in northwest Bangladesh and evaluate their
ecological hazards for aquatic plants and animals. Results
presented the most often detected pesticides that seemed
in high levels were, Quinalphos, Diazinon and
Chlorpyrifos, in sediment and water. The maximum
concentration of chlorpyrifos measured in water was
0.0091 mg/L (average of 0.002 mg/L), while this was
0.0051 mg/L for Diazinon (average of 0.0011 mg/L) for
sediment [48]. Moreover, these results showed high
chronic risk quotients (RQ>1) in sediment and water
samples for Diazinon, Chlorpyrifos, Malathion,
Fenitrothion and Quinalphos. That information is not for
groundwater entirely but gives also a complete picture of
residual pesticide levels and possibilities of poisoning in
groundwaters in Bangladesh.
Surface Water Contamination: The surface water body
can easily contaminate rather than groundwater.
Pesticides reached in nearby surface water sources
through run-off or rain-wash. Numerous studies have
been performed regarding these types of contaminations
in Bangladesh, some of those are included in Table 3.
Hossain et al. [64] showed that in Dhamrai and Savar
Sub-district, out of 27 surface water samples, Carbofuran
and Diazinon were found in surface water samples from
Savar at 0.9 and 198.7 mg/L, respectively and Malathion
was found in Dhamrai at 105.2 mg/L. In another study in
the same place, out of 12 surface water samples in the
agricultural wetland, Carbofuran residues were founded
43.2 mg/L, Carbaryl residues ranging from 4.6 mg/L to
6.3 mg/L, Cypermethrin in 3 water samples varied from
54.36 mg/L to 80.5 mg/ [64]. Islam et al. [62] collected
159
Am-Euras. J. Agric. & Environ. Sci., 21 (3): 151-167, 2021
48 samples from agricultural wet paddy fields from
different areas in Bangladesh and found water samples
from 10 sites were contaminated by Heptachlor, DDT and
Lindane (Table 3). Also Table 3 Showed that Heptachlor
was found at Dhaka, Chittagong and Magura Districts;
DDT was detected at Bogra and Rajbari; Lindane was
found at Dhaka, Noakhali, Sylhet and Shariatpur Districts;
also, the maximum level of DDT deposit was observed in
Bogura at the level of 0.5401 mg/L. Furthermore,
Chowdhury et al. [72] collected surface water samples
from 22 Districts in the country and they observed that
DDT residue exists in the surface water of Nawabganj,
Rajshahi and Feni Districts. This study was found the
highest DDT load of 8.29 mg/L. Again, they also found
that the Heptachlor deposits in Madaripur, Sunamganj
and Natore Districts with the highest concentration of
5.24 mg/L. Likewise, Chowdhury et al. [70] 16 water
samples were collected from lakes and paddy fields in
Rangpur city and these water samples carry Chlorpyrifos
ranging from 0.554 mg/L to 0.895 mg/L, Carbofuran
ranging from 0.949 mg/L to 1.671 mg/L and Carbaryl in 1
sample at 0.195 mg/L. The same study in the river water
samples found that Chlorpyrifos in 7 samples (0.477 mg/L
to 1.189 mg/L), Carbofuran in 7 samples (0.934 mg/L to
3.395 mg/L) and Carbaryl in two samples at 0.055 mg/L and
0.163 mg/L. They also found both Heptachlor and DDT
residues in surface water samples from the Sunamganj
District.
Some studies were carried out in Pond water and the
results also confirmed that this water source can be
contaminated by pesticides. Bagchi et al. [8] 20 pond
water samples were collected and observed that the
presence of Heptachlor and DDE in 1 water sample and
DDT, DDD, DDE in other samples but their level was
within the WHO standard value. In the same study, it was
also found Carbofuran residues in 10 samples but that
was also within the WHO-recognized level. Likewise,
25 pond water samples were collected by another study
from Brahmanbaria district and found Malathion in 3
samples ranging from 0.0241 mg/L to 0.0463 mg/L [74]
and other samples were not carried any pesticide residues.
Chowdhury et al. [72]; Uddin et al. [74]; and
Hasanuzzaman et al. [76] also performed the study on
pond water contamination by pesticides in various
regions of the country.
Several studies e.g., FAO [31], Sharma et al. [27], UN [78]
were shown that the water body of the Mediterranean
region, USA, South-central America, China, middle and
southeast Asia, Australia and some countries of Africa
are mostly contaminated through pesticides (Fig. 6).
Considering climate data, topography, land use patterns,
crop diversity and rates of pesticide application, the map
displays that the risk of pesticide contamination is
comparatively low in Canada, northern Europe and Russia
but increases near the tropical and equator. The warmer
and humid climate intensifies the crop pest and that
type of weather is good for agricultural activity also.
The highly water-contaminated countries through
pesticides on the map are crop-rich areas and used
15-20 kg/hectare chemical pesticides [36]. The residual
portion of it ultimately reaches into a near waterbody and
some are leached to groundwater aquifers and those
countries face serious water pollution [14].
Controlling Chemical Pesticides -Uses of IPM and
Bio-Pesticides: Uses of Integrated Pest Management
(IPM) and bio-/herbal/botanical pesticides in agriculture
are environment-friendly and
have confirmed
indications to decrease pest infestation and control the
eruption of diseases in crops. The IPM is a farming
technique that comprises manifold cropping, planting
disgusting crops in the margin of the bed,
intercropping, applying biological pest controller agents
(e.g., pheromone trap), etc. Botanical or herbal pesticides
resulting from animals, plants, bacteria, etc., have like
qualities and potentialities compared to chemical
pesticides. Another technique, pheromone traps, is a kind
of system from where insect sex pheromone releases and
attractions the opposite sex to mate. Ultimately the
harmful insects are trapped in the device where no
reproduction of the pest happens. The use of
Vermicompost is another part of IPM and this
material gradually gathered popularity in the former
community in Bangladesh. IPM in the agriculture sector
had been introduced by the government of Bangladesh
3 decades ago but the Pesticide Act, 1985 did not remark
the wording ‘bio or botanical’ and for this reason,
agro-based companies did not make IPM related tools or
bio-pesticides. Throughout the recent years, IPM and
botanical pesticides got a drive. For this reason, the
application of chemical pesticides has decreased, which
means the use of IPM and botanical pesticides increased.
The use of chemical pesticides increased vastly from 1990
to 2007 and then drops steadily which is discussed in
Section 2 of this paper.
World Scenarios: Roughly 40% of the earth’s land area
and 64% of the cultivable area of the world are at risk of
contamination from chemical pesticides [77]. But, yet now,
the maximum affected areas are not properly investigated.
160
Am-Euras. J. Agric. & Environ. Sci., 21 (3): 151-167, 2021
Fig. 6: Countries (red-marked) of high water contaminated through pesticides residue
The idea of IPM contained most of the use of
pesticides in a way that was compatible with organic
control of pests and insects but the attention of IPM
started to shift to non-pesticidal tactics in the 1980s [79].
Application of IPM policies saved USA agriculture from
500 million dollars per annum owing to decreases in
pesticide usage [80]. (On the other hand, Norway started
a pesticide reduction strategy in the year 1988 which
imposed a levied banded tax system based on toxicity at
the rate of 3.8 dollars per hectare that bring about a 54%
decrease in pesticide usage [81]. In Indonesia,
government to control the use of pesticide, decrease
pesticide subsidies and directive IPM as the national
strategy for crop protection and steadily reduced chemical
pesticide subsidies [82, 83]. From a preliminary censored
in 1986, subsidies had been removed by 1989. Thus, it is
a big opportunity for an agrarian nation as Bangladesh to
decrease the probable health hazards along with costs
due to pesticide use with the applying of IPM activities.
In Bangladesh, the IPM strategy was first in progress
from 1981 in rice crop, but it was beginning to increase
and became a popular technique among formers from
1987 through the FAO’s Inter-Country Program (IPC) [84].
The IPC-FAO affords IPM training through farmers with
the help of Farmer Field Schools. Over 1 lakh farmers have
now received a season-long practical, in-depth training on
IPM. But these figures only 0.28 % of the total 0.37 crore
cultivators of the country [85]. The IPM-skilled farmers of
Bangladesh can decrease their pesticide application by as
much as 80 % together with an increased harvest of about
10 %. Though to ensure a positive and significant result
of IPM at the national level, still, many farmers must be
skilled in IPM and besides, they should exercise IPM in
their crop fields frequently. In this case, in Bangladesh,
essential mechanisms will be recognized to ensure the
expansion and coordination for a sustainable IPM
program.
The Bangladesh government has permitted the
Balai Nashak (pesticide) Act, 2017 signifying tougher
disciplinary actions against the sale, marketing,
packaging, advertisement and storage of banded and
highly harmful pesticides. According to the existing
Pesticide Amendment - 2010, if a company is found
adulteration of pesticides, there will be 2-year custody
and termination of the company’s license. Moreover,
Bangladesh had previously passed National Food Safety
Act 2013. If all these Rules and Acts applying
appropriately, there will be a change in basic assumptions
towards pesticide uses and vending.
Other Types of Chemical Pesticides Controls: Traditional
chemical pesticides are very toxic to the environment, for
that they should use the following least toxic or safe
processes to pest control.
Baits - uses sticky or gels materials in a pest's path
when pests meet baits, they are joint with it.
Cleaning Solutions - using household cleansers
(Lysol and bleach) keep areas disinfected and deter pests.
Insect growth regulators (IGR) - IGRs stop the
maturity procedure in insects.
161
Am-Euras. J. Agric. & Environ. Sci., 21 (3): 151-167, 2021
Repellents - these are used to deter animals from
specific zones or from feeding on certain plants.
Desiccating dust - desiccating dust attack the outer
layer of an insect's body and causes the loss of water and
dry out.
Pesticidal soaps/oils - these materials are toxic to
insects and decay quickly in the environment, not leaving
residues.
Botanical pesticides – these substances are derived
from plants and have powerful effects on pests.
Concentrated liquid /powders/ solutions – natural
alkaloids, pyrroles and some synthetic less toxic
chemicals.
Rodenticide baits – anticoagulants (Coumarins and
Indandiones), Non-anticoagulants (Benzenamines) and
Zn3P2.
identified the pesticides in their water samples with more
or less concentration. So, this is the greatest threat to the
environment as well as humans and other living species.
To decrease the thriving trends of pesticide application
and thus, the increasing environmental hazard, Integrated
Pest Management (IPM) strategy can be a good solution.
It is the technique in which the pest population is
repressed under the level that causes economic injury
using all appropriate policies and methods. Another
solution to pesticide hazard is the massively uses of
herb- or bio-pesticide in crop fields to protect the pest as
well as overuse of chemical pesticides. In addition, the
finding of this study advises the essential for worldwide
developments to current pesticide guidelines and
pesticide application practices and strengthened research
efforts on the impacts of pesticides under real-world
conditions.
CONCLUSION
Bangladesh, devastatingly an agro-economy, has
followed the path of quick dispersion of a rice-based
Green Revolution Technology (GRT) over the previous
4 decades to achieve the goal of independence in food
crops. As well, the government has highlighted crop
divergence since the early 2000s to endorse agricultural
growth and export incomes. Both these strategies-driven
factors have given rise to a significant increase in the
use of pesticides and other agrochemicals. There was a
500-750% increase in the production and application of
the pesticide from mid nineteen in Bangladesh as well as
the whole world. The environmental impacts of these
hazardous substances are now reaching a serious
position in the country. Not only Bangladesh, other
agricultural countries like China, the USA, South
American, South and Middle Asia and some areas of
Africa are now facing serious environmental impacts by
pesticides. From various studies, we have explored the
rate of worldwide pesticide consumptions and highly
water contaminated countries through different two maps.
Water is the primary source of these hazardous materials
and is accumulation in the human body through a food
chain. This study found that all kinds of chemical
pesticides which are massively used in the country’s
agricultural land exist in the surface and groundwater of
several regions in Bangladesh. Especially, the
concentrations of very toxic Organochlorine insecticides
were identified as a higher level (0.01-1.20 mg/L) than the
W H O guideline value. We have explored the 15 studies
performed around the country and conducted by a
separate researcher. Among these studies, all those wares
162
Declaration
Funding: The study has not been received any funds
from any organization.
Competing Interests: The authors declare that they have
no conflict of interest.
Author’s Contributions: Islam MS participated in the
design and performance of the reviewing process
and writing the primary manuscript draft and
revise draft preparation. Mostafa MG analyzed the data,
draft the revision and finalize the manuscript for
submission.
Ethical Approval: This article does not contain any
experiment with any animal or human performed by any of
the authors. The manuscript in part or in full has not been
submitted or published anywhere and will not be
submitted elsewhere until the editorial process is
completed.
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