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Effect of processing on pesticide residues in food crops - A review

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  • PMAS-Arid Agriculture University
Processing effect on pesticide residues in food crops 379
EFFECT OF PROCESSING ON PESTICIDE RESIDUES
IN FOOD CROPS - A REVIEW
Anwaar Ahmed*, Muhammad Atif Randhawa**, Muhammad Javed Yusuf***
and Naeem Khalid****
ABSTRACT
The use of pesticides is inevitable to control the pests in different crops, fruits
and vegetable plants. It is increasing day by day in Pakistan. The persistent use
of pesticides leaves behind toxic residues on food crops. These pesticides
upon ingestion exert adverse effects on human health, in addition to disturbing
ecosystem. The organochlorine, organophosphorus, carbamates and
pyrethroid pesticides have been detected in samples of fruits and vegetables
collected from various locations of the world especially in Indo-Pakistan. Most
of the samples contained toxic residues exceeding maximum residues limits.
Experiments have been carried out to determine the reduction in pesticide
residues due to various processing techniques like washing, peeling, frying,
freezing and cooking of fruits and vegetables. Likewise treatment of food crops
with acidic or alkaline solution also minimized the pesticide residues. This
paper reviews the literature published upto the year 2009 focusing on the
injurious effects of pesticides and their degradation by processing and
chemical treatment. In this literature, it is suggested that different processing
operations can be effectively applied on fruits and vegetables to minimize the
risk of pesticides on human health.
KEYWORDS: Pesticides; residues; food crops; toxicity; Pakistan.
INTRODUCTION
In Pakistan, crop losses are very alarming which are estimated as 30-40
percent pre-harvest, 10-30 percent post harvest and 50 percent crop losses
are due to insects, weeds, diseases and rodents (21) In order to safeguard
agricultural produce from ravage of pests, use of pesticides is considered as
*Assistant Professor, Department of Food Technology, Pir Mehr Ali Shah Arid
Agriculture University, Rawalpindi, Pakistan, **Assistant Professor, National Institute of
Food Science & Technology, University of Agriculture, Faisalabad, ***Assistant Botanist,
Fodder Research Institute, Sargodha, Pakistan, ****Deputy Secretary (Planning),
Department of Agriculture, Govt. of Punjab, Lahore, Pakistan.
J. Agric. Res., 2011, 49(3)
A. Ahmed et al.
380
the only solution. Due to reason, pesticides consumption has increased
manifolds during the last two decades (29). Most of the growth in world
pesticide market is in developing countries. Globally, organophosphates
account for nearly 40 percent of total insecticide sales by value followed by
carbamates (20.4%), pyrethroids (18.4 %) and organochlorines (6.1%) (4).
Pakistan is importing a huge quantity of pesticides every year. In 1990, it
imported 13030.14 tons of pesticides; which reached to 30479.00 tons in
1995. During year 2007 the import increased to about 41406.00 tons. So the
import of pesticides is increasing day by day in the country (39).
Pesticide a necessary evil and its injudicious use
Sulfur was used as pesticide to control insects and mites 5,000 years ago. In
ancient times, Chinese used mercury and arsenic compounds to control body
lice and other pests while Greeks and Romans used oil, ash, sulfur, and other
materials to protect themselves, as well as livestock, and crops from various
pests. The cultural methods were also employed to control the pests, such as
crop rotation, tillage and manipulation of sowing dates (12).
The modern era of chemical pest control began around the time of World
War-II, when the synthetic organic chemical industry began to develop. The
first synthetic organic pesticides developed were organochlorines, such as
dichlorodiphenyltrichloroethane (DDT) in Switzerland in 1939. The DDT and
other organochlorine insecticides (cyclodiene organochlorines, aldrin and
dieldrin, endrin, endosulfan and isobenzan) were used as these insecticides
acted against insects by blocking their nervous system, causing malfunction,
tremors, and death (42). Hence, pesticides application became an essential
component of modern agriculture. Although the wide-spread use of pesticides
in Pakistan has controlled the pests, but like other countries, it has started
causing environmental problems in the area. In some areas of Punjab and
Sindh groundwater has been found contaminated and is constantly being
contaminatied due to pesticide use. There is considerable evidence that
farmers have overused and misused pesticides especially in cotton-growing
areas. It is evident from the biological monitoring studies that farmers are at
higher risk for acute and chronic health effects associated with pesticides due
to occupational exposure (39). However, pesticide use also has created
concerns regarding its effect on the environment and the potentially toxic or
carcinogenic residues remaining in the food chain (27).
J. Agric. Res., 2011, 49(3)
Processing effect on pesticide residues in food crops 381
Toxicity of pesticides
Deaths from exposure to pesticides are not uncommon. Each year thousands
of farmers, especially in developing countries, are affected by exposure to
pesticides especially those living near the farms. Recent estimates quoted by
Food and Agricultural Organization (2000) from Pesticide Action Network
(PAN) show that approximately three million people are poisoned and
200,000 die from pesticide poisoning each year. The largest number of
deaths occurs in developing countries. For example, hospital statistics in Sri
Lanka show that on average 14,500 individuals were admitted to government
hospitals and around 1500 individuals a year died from pesticide poisoning
during the period 1986–1996 (National Poisons Information Centre, 1997).
However, these figures should be interpreted with caution. It should be
pointed out that not all hospital admissions and deaths were due to
occupational poisoning but include cases of self ingestion (suicides),
accidental ingestion and homicides. Moreover, there is evidence suggesting
that some pesticides can produce immune dysfunction among animals when
exposed to pesticides (40). A study (16) showed that women who had
chronically ingested groundwater contaminated with low levels of aldicarb had
significantly reduced immune response, although these women did not exhibit
any overt health problems. However, it should be noted that study of immune
suppression potential for pesticides is still in its infancy and that the evidence
available is inconclusive (40). Even in developed countries, despite the strict
regulations and use of safer pesticides, occupational exposures may be
significant (4). It is believed that in developing countries incidence of pesticide
poisoning may even be greater than reported due to under-reporting, lack of
data and misdiagnosis (17).
The incidence and severity of ill health from pesticide-use are far greater in
developing countries than in developed countries due to many reasons. Most
of the farmers in developed countries use pesticides from a closed
environment such as an aircraft or a tractor, while farmers (who are largely
small scale farmers) in developing countries use hand sprayers, thus
increasing the incidence of direct contact with pesticides. Moreover, as noted
by WRI (4) farmers in the developing world use more insecticides, they use
them more frequently and also apply insecticides that are more toxic than
those used in developed countries. Inadequate education, training and
pesticide regulations in the use of pesticides lead to accidents, haphazard
application and over-use. Access to medical treatment is limited and most
farmers rely on homemade remedies thus increasing the severity and
duration of illnesses. Poor health and diet are other factors that are believed
to increase the incidence of illnesses from exposure to pesticides in
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382
developing countries (4). Inadequate or non-existent storage facilities, poor
living conditions and water supplies contaminated with pesticides also affect
the health of families.
Pesticide residues in raw fruits and vegetables
The organochlorine, organophosphorus and pyrethroid pesticides were
monitored in samples of fruits and vegetables procured from the whole sale
market of Karachi during July 1988 and June 1990. A total of 250 samples
were screened out of which 93 samples were found to be contaminated with
variety of pesticides. Forty five samples were found to contain residues above
maximum residues limits (MRLs) proposed by FAO/WHO while 48 samples
contained residues well within permissible limits. In remaining samples, no
pesticides residue was detected (39). In 2001 a total of 315 samples
representing a wide variety of produce were tested. Of these 73 percent
samples were fresh produce and 27 percent were processed foods. Pesticide
residues were found in 47 percent samples of fresh produce and 7 percent of
processed foods samples (41). Frank et al. (18) surveyed Ontario grown
vegetables in Canada for pesticide residues during 1980-85. A total of 354
samples were screened. Most of the samples contained residues well within
maximum residues limits (MRLs) while the limits were exceeded in only a
small number of samples. In 1998 a total of 180 samples of vegetables were
tested, 89 percent were fresh produce and 19 percent were processed
vegetables. Pesticide residues were found in 35 percent of fresh produce
samples and 10 percent of processed vegetables (39, 41).
EFFECT OF PROCESSING ON PESTICIDE RESIDUES
Experiments were carried out to determine changes in pesticide residues due
to washing, peeling and cooking process (blanching and frying). The purpose
of these experiments was to assess the stability of pesticides in vegetables
and their products. There are strong evidences that through processing of
vegetables pesticide residues decrease (25, 33, 34, 37). Unit operations in
processing typically include washing the raw product with large volumes of
water, frequently using high-pressure sprays and often incorporating
surfactants or other washing aids; peeling the product mechanically with
knives, abrasive disks, or water; blanching with hot water or steam; and in
case of canned or cooked foods, cooking of the product at temperatures at or
above the boiling temperature of water. Thus, residue that may be present
was subjected not only to physical removal by washing or peeling but also
acid or base hydrolysis and thermal degradation (11).
Washing
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Processing effect on pesticide residues in food crops 383
Surface residues are amenable to simple washing operations whereas
systemic residues present in tissues will be little affected. For example, highly
pola and systemic methamidaphos was the only pesticide whose residues
could not be removed from field tomatoes by washing. There is evidence for a
variety of crops and pesticides that the proportion of residue that can be
removed by washing declines with time (19, 33, 34, 36, 37). This has been
interpreted as being due to residues tending to move into cuticular waxes or
deeper layers. For example the fractions of fenitrothion or methidathion
residues on cauliflower that could be removed by washing or blanching were
inversely proportional to the days after spray application (38).
Hot washing and blanching are more effective than cold washing and the
effectiveness may be further improved by detergent (19). Blanching removed
82 percent of methidathion residues from cauliflower and did not show any
effect of withholding period as compared to the lower proportion of residues
removed by washing (30). Domestic rinsing is less effective compared to
thorough commercial washing. Hot caustic washes used in some commercial
peeling operations can efficiently remove and degrade residues of
hydrolysable pesticides (15).
Peeling, hulling and trimming
The majority of insecticides or fungicides applied directly to crops undergoes
very limited movement or penetration into the cuticle. Therefore, residues of
these materials are confined to the outer surfaces where they are amenable
to removal in peeling, hulling or trimming operations (20, 35). Peeling fresh
fruits such avocado, bananas, citrus, kiwifruit, mango and pineapple achieves
virtually complete removal of residues from the fruit. There is substantial data
showing non-detectable residues in pulp of citrus and edible portion of other
fruits that support these conclusions. For example, supervised field trials of
pirimiphos-methyl on various citrus crops gave non-detectable (< 0.03 mg/kg)
residues in the pulp compared to residues in the peel (0.5 to 5 mg/kg) (5).
Post harvest dipping trials were conducted on pineapple with the fungicide
triadimefon which has some trans-laminar action. Residues in the flesh were
only 0.5 to 1 percent of those in the peel (20). Under Codex, MRL’s are based
on the whole fruit which is appropriate for assessing compliance with Good
Agricultural Practices (GAP) (39). These MRLs are of limited significance in
assessing exposure to pesticides from consumption of fresh fruits which are
peeled or juiced. However, apples and tomatoes may be consumed either
whole or after peeling.
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384
Residues of systemic pesticides can enter the flesh of crops. Following early
season soil incorporation of phorate, residues in washed whole potatoes of
0.37 mg/kg (parent plus oxidation products) were reduced only by 50 percent
through peeling (5). Similarly disyston residues in potatoes were reduced only
35 percent by peeling (8) whereas residues of the much more lipophilic
chlorpyrifos were completely removed in the peels (24). The hulls of cereal
grains generally contain the majority of pesticide residues from any field
treatments. Residues of parathion in oat or rice grains were reduced eight
folds on hulling (5). Pirimiphos methyl residues in rice were reduced 70
percent and 90 percent by husking and polishing, respectively (13). Husking
of corn (maize) removed 99 percent of the residues from field treatments with
tetrachlorvinphos (14).
Cooking and canning
The processes and conditions used in food cooking are highly varied (25).
The details of time, temperature, degree of moisture loss and whether the
system is open or closed are important to the quantitative effects on residue
levels. Rates of degradation and volatilization of residues are increased by
the heat involved in cooking or pasteurization. For example, in a study on
radio labeled chlorothalonil residues, cooking under open conditions resulted
in 85 to 98 percent losses by volatilization. Cooking under closed conditions
resulted in hydrolysis with 50 percent of the chlorothalonil being recovered
unchanged on the crop and hydrolysis product being found in the liquor (5).
For compounds that are of low volatility and relatively stable to hydrolysis
such as DDT and synthetic pyrethroids, losses of residues through cooking
may be low and concentrations may actually increase due to moisture loss.
However, deltamethrin has been reported to have a half-life of 9 minutes in
boiling water and residues were reduced by 66 percent by cooking of various
vegetables (10).
Commercial processing in its various forms combines elements of washing,
peeling, juicing, cooking and concentration. Processing of whole tomatoes
with vinclozolin residues of 0.73 mg/kg gave residues in canned juice, puree
and ketchup at level of 0.18, 0.73 and 0.22 mg/kg, respectively (5, 25). In this
case the relatively stable fungicide vinclozolin was carried through the
process in significant amounts. Only 13 percent of parathion residues on
tomatoes were found in canned juice or ketchup.
Stir-frying and freezing
Pesticide residues can be effectively decreased by stir-frying (32, 45). These
can be reduced upto 49 and 53 percent by peeling and frying (33). Freezing
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Processing effect on pesticide residues in food crops 385
of food is a common method of food preservation which slows both food
decay and most chemical reactions. Freezing of tomatoes decreased the
pesticide residues from 5 to 26 percent after six days and 10 to 31 percent
after 12 days of pesticide contamination (1). Zhang et al. (45) estimated the
pesticides residue levels in cabbage after preserving in refrigerator. In some
vegetables, pesticide residues are decreased after refrigeration. By
increasing the time of refrigeration there is gradual increase in reduction of
pesticide residues, After three days of freezing, HCB, lindane, DDT,
dimethoate, profenofos and pirimiphos-methyl decreased by 4.91, 6.32, 4.07,
13.0, 11.5 and 9.35 percent, respectively (15).
EFFECT OF CHEMICAL SOLUTIONS ON PESTICIDE RESIDUES
Acidic solutions
Soaking in acidic solution like citric acid, ascorbic acid, acetic acid and
hydrogen peroxide at a concentration of 5 and 10 percent for 10 minutes
indicates proficient reduction of pesticide residues. Acidic solutions give more
pesticide dissipation than neutral and alkaline solutions. The acidic solutions
of 5 and 10 percent eliminated pesticide residues completely while, citric and
ascorbic acid solutions of 5 and 10 percent eliminated pesticide residues upto
80 percent (43). Some other scientists (14, 31, 36) also reported that partial
removal of residues was affected by the washing operation (water and/or
acetic acid, sodium chloride).
Neutral solutions
Sodium chloride (NaCl) solution is largely used to decontaminate the
pesticide residues from different fruits and vegetables. There are several
studies (14, 31, 36, 46) to prove the efficacy of salt water washing for
dislodging the pesticides from fruits and vegetable surfaces. In this process,
samples of chopped fruits and vegetables were put in a beaker containing 5
and 10 percent NaCl solution for 15 minutes. The samples were gently
rubbed by hand in salt solution and water was decanted. Twenty eight to 93
percent reduction in organochlorines and 100 percent organophoshates
removal was achieved by using 5 and 10 percent NaCl solution (43). The
percentage reduction in pesticide residues increases with the gradual
increase in concentration of solutions (1, 22). NaCl with 2, 4, 6, 8 and 10
percent solution caused 20 to 90 percent reduction in pesticide residues.
Similarly 18 to 65 percent loss in pesticide residues was reported by Soliman
(37) by using 2, 4, 6, 8 and 10 percent acetic acid solution.
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386
Alkaline solution and ozonation
Solutions of NaOH, acetic acid, potassium dichromate and soap are used as
decontaminating agents. Dipping of fruits in NaOH solution removed 50 to 60
percent surface residues of pyrethroids compared to 40 to 50 percent
removal by hydrolytic degradation with NaOH and a detergent solution
removed 50 to 60 percent residues (6).
Ozone because of its powerful oxidizing property is effectively applied in
drinking water and waste water treatment. Recently some scientists found
that certain pesticides like 2, 4-dichlorophenoxyacetic acid, carbofuran,
phorate, chlorophenylurea, can readily be degraded in aqueous solution by
ozone (7, 9, 26). Ozonation is a safe and promising process for the removal
of pesticides from aqueous solution and vegetable surface under domestic
conditions. Tap water treatment alongwith ozonated water treatments
significantly reduced the pesticide residues on vegetables, as compared to
no-wash treatment (41).
CONCLUSION
From the extensive review on the use and fate of pesticides during food
processing, it is concluded that pesticides are inevitable part of the agriculture
but their indiscriminate use can cause serious health problems. In a
developing country like Pakistan there is a great need to regulate the use of
pesticides where the extensive use of pesticides is causing serious health
and alarming environmental problems. To minimize the risk of pesticides on
health different processing operations are applied on fruit and vegetable
crops that reduce the pesticide residues below the risk level. It is further
concluded that treatment of vegetables with acidic and alkaline solutions can
effectively minimize the pesticide residues. There is a need to educate the
consumers through media.
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... Mitigating the adverse effects of pesticides requires a comprehensive approach that emphasizes proper education and training for farmers. This includes educating farmers on safe pesticide usage, handling, and storage practices, as well as providing training on integrated pest management strategies(Ahmed et al., 2011). Ensuring food safety remains a top priority for governments and various private and international organizations. ...
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Pesticide residues have become an escalating concern in Pakistan, raising significant risks to both public health and the environment. This review overviews the current status of pesticide contamination in the country, with a specific focus on residue levels in relation to Maximum Residue Limits (MRLs) and a comparative analysis with regional and global counterparts. Several studies reveal that 30% to 70% of tested food products, including fruits, vegetables, and animal-derived products, especially in Punjab and Sindh, exceed established MRLs. This level of contamination is considerably higher than in neighboring countries such as India, where MRL exceedance ranges from 20 to 30%, and Bangladesh, which reports lower levels due to stricter regulatory efforts. In comparison, developed countries, including those in the European Union and the United States, report less than 5% of food samples exceeding MRLs, often falling below 1% due to stringent safety standards. The high prevalence of pesticide residues in Pakistan poses severe health risks, including neurological disorders, reproductive problems, and cancer, particularly in vulnerable groups like children and pregnant women. Key factors contributing to these elevated pesticide levels include insufficient knowledge of safe pesticide use, the unregulated application of banned or expired products, improper safety protocols, and malfunctioning equipment. A prevailing reliance on pesticides as the sole pest control method further hinders the adoption of Integrated Pest Management (IPM) strategies. In conclusion, pesticide residue levels in Pakistan are above permissible MRLs compared to regional and global standards, underscoring the need for urgent improvements in pesticide regulation, enforcement, and the promotion of sustainable pest control methods like IPM to better protect human health and the environment. Graphical Abstract
... Around the time of World War II, the synthetic organic chemical industry started to grow, introducing the modern era of chemical pest control. Organochlorines, such as dichlorodiphenyltrichloroethane (DDT), were the first synthetic organic insecticides to be produced(Ahmed et al., 2011). ...
... These health risks include headaches, nausea, irritation, vomiting, abdominal pain etc. Several studies have demonstrated that vegetables absorb pesticides internally when they are sprayed on them and cause adverse effects when consumed by humans and animals [1,2]. The rate of vegetable production in Bangladesh has been increased and this rate is higher than the previous decade. ...
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Fresh salad vegetables have become a convenient part of daily diet of people nowadays because of their nutritional enrichment. Although raw vegetables are compact source of high nutritional values, these vegetables are sometimes detrimental to human health because of being potential route of human exposure to pesticide contaminants. This study is focused on the prevalence of pesticide contaminants in daily consuming common salad vegetables. The study was conducted to observe six pesticides residue (Cypermethrin, Mancozeb, Malathion, Rovral, Imazalil, Endrin) using gas chromatography mass spectrometry (GC-MS) in five types of raw consuming vegetables that are sold in the local markets of Rajshahi City. The findings suggest that almost all the vegetables of three markets were contamination free. The residual level of all six targeted pesticides had not been detected. Thus, this study suggests that the application of pesticides in the fields of Rajshahi City is within safe limit.
... That may be because the bulk of pesticides and fungicides on crops directly move or penetrate the cuticle very little. As a result, these materials' remnants are restricted to the exterior surfaces, where peeling, hulling, or trimming procedures can remove them (Ahmed et al., 2011). When fruits or vegetables are peeled, even pesticides that have gotten into the cuticles of the produce are removed (Abou-Arab, 1999). ...
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Pesticides are widely used in food production to increase food security, although they can adversely affect consumers. Pesticide residues have been found in various fruits and vegetables, both raw and processed. Therefore, the study investigates the presence of pesticide residues such as systemic pesticides (Pyridaben and alpha-cypermethrin) and non-systemic pesticides (azoxystrobin and propamocarb hydrochloride) in commonly consumed fruits and vegetables, specifically okra, grapes, dates, and tomato. The researchers also evaluate the effectiveness of various processing methods in reducing pesticide residue levels, such as washing with water and other solutions such as acetic and citric acids (2%), peeling, blanching, alkaline and sulfuring treatment, drying and concentration at high temperature. Our finding showed that the processing method steps could reduce pesticide residuals with different reductions %, which are affected by the physical and chemical properties of pesticides, processing steps conditions and the nature of the fruit or vegetable. Even after some processing steps, samples still had residue levels exceeding the Maximum Residue Limits (MRLs), such as washing, peeling, juicing and alkaline or sulfating treatment steps. Indicating that consumers may still be exposed to unsafe levels of pesticides. Otherwise, at the end of processing methods such as blanching, drying and concentration, all final products become almost free of pesticide residuals. The study concludes that processing methods can reduce the levels of pesticide residues or eliminate them.
... Methods have been developed to remove pesticide residues from food plants (e.g., food processing and cooking) [16][17][18]. However, cooking can severely impair the antioxidant nutrients in food [19]. ...
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In the present study, we attempted to use melatonin combined with germination treatment to remove pesticide residues from contaminated grains. High levels of pesticide residues were detected in soybean seeds after soaking with chlorothalonil (10 mM) and malathion (1 mM) for 2 hours. Treatment with 50 μM melatonin for 5 days completely removed the pesticide residues, while in the control group, only 61–71% of pesticide residues were removed from soybean sprouts. Compared with the control, melatonin treatment for 7 days further increased the content of ascorbic acid (by 48–66%), total phenolics (by 52–68%), isoflavones (by 22–34%), the total antioxidant capacity (by 37–40%), and the accumulated levels of unsaturated fatty acids (C18:1, C18:2, and C18:3) (by 17–30%) in soybean sprouts. Moreover, melatonin treatment further increased the accumulation of ten components of phenols and isoflavones in soybean sprouts relative to those in the control. The ability of melatonin to accelerate the degradation of pesticide residues and promote the accumulation of antioxidant metabolites might be related to its ability to trigger the glutathione detoxification system in soybean sprouts. Melatonin promoted glutathione synthesis (by 49–139%) and elevated the activities of glutathione-S-transferase (by 24–78%) and glutathione reductase (by 38–61%). In summary, we report a new method in which combined treatment by melatonin and germination rapidly degrades pesticide residues in contaminated grains and improves the nutritional quality of food.
... The effects of household processing on pesticide residues showed a reduction of pesticide residues in various vegetables (Ahmed et al. 2011;Calumpang 2014;Chung 2018;Đorđević and Đurović-Pejčev 2016;Kaushik et al. 2009). Pesticide residues can be lowered significantly by simple household practices like washing, peeling, and cooking operations (Soliman 2001;Zohair 2001). ...
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A field study was conducted to investigate the dipping and spraying of bitter gourd fruits with insecticide solution at the National Crop Protection Center, University of the Philippines Los Baňos in January 2019. Bitter gourd fruits were sprayed with recommended dose and double the recommended dose of commercial products containing chlorpyrifos, profenofos and cypermethrin. The field trial results revealed all pesticide residues in both applications, after the post-harvest interval of 10, 7, and 7 days, respectively did not exceed the CODEX or ASEAN Maximum Residue Limits (MRLs) of several fruiting vegetables. A pesticide residue survey of 34 bitter gourd market basket samples were analyzed for various insecticide residues. A variable range of detectable insecticide residues were detected with chlorpyrifos, cypermethrin, endosulfan and profenofos. The effects of home processing were evaluated and the results demonstrated that washing with mild detergent solution was consistently a good home preparation for reducing residues substantially on bitter gourd fruits. In addition, soaking in vinegar alone, soaking in vinegar and boiling, as well as grilling also contributed to reduction of residues. A combination of home processing steps should be able to address food safety concerns. The dietary risk offered by dipping bitter gourd in chlorpyrifos, cypermethrin and profenofos is very low and similar in magnitude with that of spraying. The following maximum residue levels are recommended in bitter gourd: 0.2 mg/kg for chlorpyrifos and cypermethrin and 0.5 mg/kg for profenofos. Additional pesticide residue trials in the field need to be conducted to support an ASEAN MRL recommendation.
... This is mainly attributed to absence of spray drift, direct exposure to sunlight and precipitation under polyhouse than open field condition. Dissipation of pesticides under polyhouse is generally slower than open field due to prevailing factors such as cooler climate and limited sunlight penetration inside the polyhouse (Holland and Phil 2003;Gavrilescu 2005;Parvej et al. 2010;Ahmed et al. 2011) . ...
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Liquid chromatography mass spectrometry (LC-MS)-based detection of flonicamid, imidacloprid and 6-chloronicotinic acid residues was validated and analysed in capsicum fruit, processed products and soil. The standard concentrations (0.0025 to 0.25 μg mL⁻¹) of insecticides had a good linear curve (r²>0.99). Limit of detection and limit of quantification values were 0.0025 and 0.01 mg kg⁻¹, respectively. The accuracy (80.53 to 100.33 %) of capsicum matrices and soil (89.41 to 100.52 %) and precision (RSD <10%) were established. Dissipation of imidacloprid (20 and 40 g a.i. ha⁻¹) and flonicamid (75 and 150 g a.i. ha⁻¹) at single (X) and double dose (2X) was studied under open field and polyhouse conditions. Under open field conditions, the flonicamid and imidacloprid residues persisted with half-life of 1.98, 2.90 days (X) and 2.80, 3.14 (2X) days, respectively. While under polyhouse conditions, the flonicamid and imidacloprid residues persisted with a half-life of 2.84, 3.66 (X) and 3.24, 3.97 (2X) days, respectively. The metabolite, 6-CNA, was not detected in any samples under open field and polyhouse condition. Among decontamination treatments, cooking in boiling water for 10 minutes reduced 78 to 81.60 percent of imidacloprid and flonicamid residues in both doses. The estimated dietary risk assessment of imidacloprid and flonicamid residues (RQ <1) indicated that the risk is within the acceptable limit. In farmgate capsicum samples, residues of flonicamid (7 samples) and imidacloprid (11 samples) were detected. Market samples of capsicum products (powder, flakes and sauce) were not detected with residues of selected insecticides. Graphical Abstract
... In different studies of organophosphorous insecticides, it was reported that OPs are unstable to heating in aqueous solutions (Fernandez -Cruz et al., 2006). For compounds that are of low volatility and relatively stable to hydrolysis such as synthetic pyrethroids, losses of residues through cooking may be low when compared to organophosphates and concentration may sometimes increase due to moisture loss (Ahmed et al., 2011). Process that normally occur during cooking are volatilization, hydrolysis and thermal breakdown (Yang et al., 2012). ...
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Abstract In order to understand the ecological details of short neck clam habitat, different parameters were taken out monthly during April 2009 to September 2010 from three stations of Ashtamudi Lake. Variation of water temperature, salinity, pH, dissolved oxygen, total suspended solids, nutrients (phosphate, nitrate, nitrite, and silicate) and chlorophyll were monitored. The short neck clam population density was also recorded. Clams were present in the site with water temperature between 26.90C and 32.50C and salinity between 15 ppt and 32.5 ppt. The pH ranged from 7.2 to 8.1 and dissolved oxygen concentration from 2.9 to 7.3 mgl-1. Minimum and maximum values of chlorophyll were 9.1 µgl-1 and 22.2 µgl-1 respectively. The nutrient analysis showed that all nutrients registered maximum values during monsoon months. Population density was highest in March 2010. The male: female ratio was dominated by the males.
... The situation is much critical in countries where water resources are limited, and lives are restricted to utilize contaminated water for various purposes. Therefore, it is an acute need to come up with an efficient and cost-effective technology for the removal of these toxins from contaminated water (Ahmed et al., 2011;Khan et al., 2015a). ...
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Emerging Trend in Biochemistry Volume I is significant applicable in the field of Chemical Science and Biological Sciences The entrance to every area of biological science is biochemistry. It's a really useful and interesting field. The study of life's molecules is known as biochemistry. Our knowledge of the molecular basis of life is expanding at an astounding rate. It is challenging to include all of the relevant material in a single compilation. The user will become discouraged due to its bulk if they have completed it at all. The process of condensing a vast amount of literature into a tiny, useful book is then considerably more difficult. Based on the ever�improving experimental accomplishments of biologists and biochemists, biochemical knowledge is constantly updated and recorded in books. The field of biochemistry is rapidly and consistently moving from the laboratory to the living sciences. As a result, in order to comprehend the principles of biological chemistry, we have selected particular subjects and information that are significant and pertinent. It addresses topics including biochemistry, phytochemistry, and the active ingredients in Indian medicinal herbs. Topics covered include organic and inorganic compounds, Qsar: A Useful Tool of Computational Chemistry for Designing New Drug and Predicting Their Biological Activities, and Inorganic Metal Oxide-Polymer Nanocomposites for Near Infra-Red. There, it also discusses medicinal chemistry and computational chemistry. By building a link between the chemical sciences and other fields of study, this book facilitates fresh research in the area. All chemistry students should perform the experiments described in the boom chapters. Additionally, they are an excellent place to start for a course on qualitative and quantitative analysis. The bio sciences are becoming more and more multidisciplinary fields of study. The multidisciplinary field of life sciences integrates various academic disciplines to address intricate problems that are broadly associated with intricate biological systems. Emerging countries have been getting ready to compete on the global stage in the biological sciences in recent years. Extensive, multidisciplinary, and current knowledge and understanding is required due to the exponential growth in scientific information and the speed at which discoveries are made. The book attempted to provide a large amount of information in an easily accessible way from the broad and constantly developing subject of life sciences. This book covers a number of themes in both the basic and applied sciences and the life sciences. This book's chapters provide information on current trends and cutting-edge research in the organic sciences. This book provides more contemporary approaches and utilizes this technology to recognize some of the basic problems facing the organic sciences today and to reach the practicability of biotechnology. An important area of the life sciences is the interaction between the organic and inorganic components of the environment. This book, which includes insightful book chapters by distinguished scientists, academicians, and researchers, will undoubtedly be used as a source of nearly all information for upcoming new research projects in the chemical sciences and other fields by researchers in the future
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Food safety is an area of growing worldwide concern on account of its direct bearing on human health. The presence of harmful pesticide residues in food has caused a great concern among the consumers. Hence, world over to tackle food safety issues, organic farming is being propagated. However, due to several reasons, diffusion and acceptance of this approach in developing countries has been very slow. Therefore, it is important in the transient phase that some pragmatic solution should be developed to tackle this situation of food safety. Food processing treatments such as washing, peeling, canning or cooking lead to a significant reduction of pesticide residues. In this background this paper reviews the common food processing operations along with the degree of residue removal in each process. The processes reviewed include: baking, bread making, dairy product manufacture, drying, thermal processing, fermentation, freezing, infusion, juicing, malting, milling, parboiling, peeling, peeling and cooking, storage, storage and milling, washing, washing and cooking, washing and drying, washing and peeling, washing peeling and juicing and wine making. Extensive literature review demonstrates that in most cases processing leads to large reductions in residue levels in the prepared food, particularly through washing, peeling and cooking operations.
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Controlled applications of DDVP (Dichlorvos) and diazinon were carried out on cucumbers grown in two different greenhouses at different times. The first group of samples was collected 4 h after the application and the second group was collected 4 days later, which was the mean cropping period applied in this region following maturation of the cucumber plant. Additionally, control samples were collected before application. The effects of washing, peeling and predetermined storage periods, at 4 °C for 3 and 6 days, on the reduction of residue levels in the plant tissues were investigated in the two groups. A gas chromatographic method, using acetone, dichloromethane and petroleum ether, as extraction solvents was used to analyse residual DDVP and Diazinon in cucumbers, with obtained recoveries greater than 81%. DDVP and Diazinon were determined by gas chromatography–electron capture detection (GC–ECD) equipped with a 5% phenylmethylpolysiloxane-coated fused-silica capillary column.Results showed that residue levels in samples, which were collected after 4 days following the pesticide application, were significantly lower than the samples collected after 4 h subsequent to the pesticide application. Culinary applications, such as washing and peeling and refrigeration storage, were also effective in reducing the residue levels.
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Effect of washing, peeling and cooking on endosulfan residue (ER) levels was determined in winter (spinach, cauliflower, potato) and summer vegetables (brinjal, tomato, okra) grown under controlled supervised field trials. Highest ER was found at raw stage in brinjal (2.43 mg/kg) followed by okra (1.83 mg/kg) and spinach (125 mg/kg) and lowest in potato (0.177 mg/kg). ER in vegetables was found to be reduced as follows: washing, 15-30; peeling, 60-67; and cooking, 13-35%. High levels of ERs exceeding maximum residue limits (MRLs) were observed in brinjal and tomato samples at raw stage. However, vegetable household processing reduced ER below the MRLs.
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Apples, treated with captan for disease control in a commercial orchard in Quebec, Canada, were collected and sorted into post-harvest preparation types (no preparation; rinse; rinse and peel). Captan residues were greatest (25.5-5100ng/g) in apples with no post-harvest preparation and lowest (0.146-136ng/g) in apples that had been rinsed and peeled prior to extraction and analysis. Residues were significantly lower (p=0.003) in apples that had been rinsed prior to extraction than in apples with no post-harvest preparation. Similarly, apples subjected to rinsing and peeling had significantly lower captan residues than had apples that had been rinsed alone (p<0.0001). Although captan residues in rinsed apples were approximately 50% lower than those in apples that received no post-harvest preparation, the reduction associated with peeling of apples was much greater (98%). Estimated mean captan intakes resulting from consumption of raw apples were established and single day intakes, based on apples with no preparation, ranged from 2.58μg/kg in females >70 years to 9.48μg/kg for individuals aged three years (at this age no distinction is made between males and females). Mean intakes estimated using rinsed and peeled apples were approximately two orders of magnitude lower than intakes estimated using apples with no post-harvest preparation, demonstrating the effect of post-harvest preparation on captan intakes. Mean captan intake estimates from all post-harvest preparation types were well below the World Health Organization acceptable daily intake of 100μg/kg/day, based on raw apple consumption. Crown Copyright © 2008. Published by Elsevier Ltd. All rights reserved.
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Tomatoes, sweet corn, and green beans were treated with Gardona and green beans were also treated with Azodrin, applied within 24 hours of crop harvesting. The harvested crops were canned by commercial methods. Pesticide residues were determined on samples withdrawn at appropriate points in the canning process. Approximately 99% of the residue on corn ears was removed in the husking process; canned corn contained less than 0.1 p.p.m. of Gardona. Washing removed nearly 50% of the Gardona residue from tomatoes. Tomato juice, heated at 100° C. for 30 minutes, contained residues of 0.03 to 0.09 p.p.m. of Gardona, while canned tomatoes, heated at 100° C. for 45 minutes, contained 0.01 to 0.03 p.p.m. of Gardona. A cold wash and hot blanching of green beans removed 90% of the Gardona residue and canned beans contained less than 0.01 p.p.m. of Gardona. The cold wash and blanching removed 33 to 53% of the Azodrin residue from green beans. Canned green beans contained 0.01 to 0.28 p.p.m. of Azodrin.
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Tomatoes grown on three separate plots were treated with DDT, malathion, and carbaryl. After harvesting, they were prepared for serving by commercial canning, home canning, and kitchen procedures and residue determinations were made at appropriate points. Commercial canning and juicing operations removed virtually all DDT, malathion, and carbaryl residues. Home canning of whole tomatoes and tomato juice removed all but trace amounts of DDT and malathion. Approximately 8% of the carbaryl residue remained in the canned whole tomatoes and 23 % remained after the home canning of juice. Home cooking removed 85% of the DDT residue, 96% of the malathion residue, and 69% of the carbaryl residue. The raw, unwashed fruit stored at 55° F. suffered no significant decrease in DDT or carbaryl; however, an apparent malathion decrease of 30 % was noted in a 7-day storage period.
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The present study investigated the degradation of four pesticides by low-concentration of dissolved ozone in order to establish the effect of operational parameters. The results indicated that dissolved ozone (initial concentration of 1.4 mg/l) was effective to oxidize 60–99% of 0.1 mg/l aqueous diazinon, parathion, methyl-parathion and cypermethrin shortly within 30 min. The feasibilities of applying low dissolved levels of ozone in water (1.4–2.0 mg/l) to remove the target pesticides residing on vegetable surface (Brassica rapa) were studied. Ozonated water was mostly effective in cypermethrin removal (>60%). The efficacy highly depended on the dissolved ozone levels. Higher temperature enhanced the efficacy in pesticide removal; however, the solubility of ozone in water is inversely proportional to temperature. The maximal efficacy for diazinon removal was detected to be at 15–20 °C. Major limitation factors for residual pesticide removal are temperature, concentration of ozone gas applied and concentration of dissolved ozone established.
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Solutions of the herbicide 2,4-dichlorophenoxyacetic acid (2,4-D) with concentrations up to near saturation at pH 3.0 and at 25 °C have been treated with ozone and ozonation catalyzed with Fe2+ and/or UVA light. Direct ozonation yields a slow depollution, while all contaminants are completely removed under UVA irradiation. The highest oxidizing power is achieved when Fe2+ and UVA light are combined, since greater amounts of oxidizing hydroxyl radical are generated and Fe3+ complexes are photodecomposed. The initial mineralization rate is enhanced when herbicide concentration increases and more hydroxyl radicals are produced by the catalyzed ozonation processes. The herbicide decay always follows a pseudo first-order reaction. Reverse-phase chromatography allows the detection and quantification of aromatic intermediates such as 2,4-dichlorophenol, 4,6-dichlororesorcinol and chlorohydroquinone. In all treatments, fast dechlorination reactions take place leading to chloride ion accumulation in the medium. The evolution of generated carboxylic acids such as glycolic, glyoxylic, maleic, fumaric and oxalic has been followed by ion-exclusion chromatography. Only oxalic acid remains stable in the O3 system, being quickly mineralized to CO2 by hydroxyl radicals formed in the O3/UVA one. A high stability of oxalic acid in the O3/Fe2+ system has also been found, since it yields Fe3+-oxalato complexes. These species are photodecarboxylated under UVA irradiation in the O3/Fe2+/UVA system. A possible reaction pathway for 2,4-D mineralization involving all intermediates detected is proposed.
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The effect of washing, peeling and cooking on residue levels of chlorpyrifos and 3,5,6-trichloro-2-pyridinol (TCP) in winter (spinach, cauliflower, potato) and summer vegetables (eggplant, tomato, okra) was determined. Analysis was carried out by capillary gas chromatography (DB-5MS capillary column) with mass selective detection. The samples were collected from trials conducted under controlled conditions as well as from the farmer's field. In supervised field trials, the highest chlorpyrifos residue was found at raw stage in spinach (1.87 mg kg-1) followed by okra (1.41 mg kg-1) and eggplant (1.25 mg kg-1). The lowest residue of chlorpyrifos was recorded in cauliflower (0.036 mg kg-1). The chlorpyrifos residue reduced from 15 to 33% after washing, 65-85% post-peeling and cooking further lowered it from 12% to 48% in all the tested vegetables; while an increase in TCP concentration was observed during heat treatment. Out of 267 vegetable samples collected from the farmer's field, 225 samples contained detectable residues representing 84% rate of contamination. About 6% of samples contained chlorpyrifos residues above maximum residue limits (MRLs). However, vegetable processing reduced the chlorpyrifos residue below the MRL.
Article
Aldicarb, a carbamate pesticide, has been a known groundwater contaminant in Wisconsin since 1981. To assess the effects of chronic ingestion of low-level aldicarb-contaminated groundwater (less than 61 ppb) on the immune function of humans, we identified 50 women, ages 18 to 70, with no known underlying reason for immunodysfunction. Twenty-three of these women (exposed group) consumed groundwater with detectable levels of aldicarb, and 27 (unexposed group) consumed water from a source with no detectable levels of aldicarb. Data were collected on each woman's health status, immune function, and fluid intake. Exposed women as compared with unexposed women showed an elevated stimulation assay response to the antigen Candida (P less than 0.02, t test). The exposed group had increased numbers of T8 cells (P less than 0.05, t test), an increased percentage of total lymphocytes as T8 cells (P less than 0.02, t test), and a decreased ratio of T4:T8 cells (P less than 0.02, t test). Our results suggest an association between consumption of aldicarb-contaminated groundwater and abnormalities in T-cell subsets in women with otherwise intact immune systems.