African Journal of
Agricultural Research

  • Abbreviation: Afr. J. Agric. Res.
  • Language: English
  • ISSN: 1991-637X
  • DOI: 10.5897/AJAR
  • Start Year: 2006
  • Published Articles: 6865

Full Length Research Paper

Assessment of the parasite load of lettuce, tomato and cucumber from some large vegetables production sites in Mali

Sanata Traore
  • Sanata Traore
  • Faculty of Sciences and Techniques; University of Sciences, Techniques and Technologies of Bamako, Mali, P. O. Box E 3206, Bamako, Mali.
  • Google Scholar
Mamadou Weleba Bagayoko
  • Mamadou Weleba Bagayoko
  • Faculty of Sciences and Techniques; University of Sciences, Techniques and Technologies of Bamako, Mali, P. O. Box E 3206, Bamako, Mali.
  • Google Scholar
Fasse Samake
  • Fasse Samake
  • Faculty of Sciences and Techniques; University of Sciences, Techniques and Technologies of Bamako, Mali, P. O. Box E 3206, Bamako, Mali.
  • Google Scholar
Amadou Hamadoun Babana
  • Amadou Hamadoun Babana
  • Faculty of Sciences and Techniques; University of Sciences, Techniques and Technologies of Bamako, Mali, P. O. Box E 3206, Bamako, Mali.
  • Google Scholar


  •  Received: 16 August 2021
  •  Accepted: 23 September 2021
  •  Published: 31 October 2021

 ABSTRACT

Fresh vegetables are an important part of a healthy diet. Consumed raw, they could be agents of transmission of intestinal parasites. The frequency and variability of parasites eggs on thirty-two samples each of lettuce, tomato and cucumber form irrigated vegetable farms in Bamako, Kati, Baguineda, Samanko, Sikasso and Niono were evaluated. The parasite load was assessed using Uga et al. method, which consist the counting of parasite eggs and cysts in 100 g of vegetable. The overall prevalence of parasitic contamination of vegetables was 20.83% of which 41.66% for lettuce and 16.66% for tomato. Cucumber was free of parasites eggs. Parasites found on the vegetables were Entamoeba coli and Trichomonas intestinalis (24.19% each), Ascaris lumbricoides (13.25%), Giardia intestinalis (12.9%), Balantidium coli (11.29%), Entamoeba histolitica (7.26%), Fasciola hepatica (3.23%), Trichinella spiralis (1.61%), Ancylostoma duodenale and Schistosoma intercalatum (1.04% each). The frequency of parasites on lettuce was 83.33% each in Bamako and Niono; 50% in Kati; 16.66% each in Baguineda and Samanko and 0% in Sikasso. Consumption of vegetables contaminated by parasites can cause a health risk for consumers.

Key words: Parasitic contamination, lettuce, tomato, cucumber, health risk.


 INTRODUCTION

Vegetables are an excellent source of vitamins, dietary fiber and minerals. Their consumption reduces the risk of cardiovascular diseases, strokes and cancers (Anand et al., 2015; Aune et al., 2017). Despite the importance and increase of the consumption of vegetables around the world, their production faces challenges, in  particular  the low availability of cultivable land in the urban and peri-urban areas of cities, the use of untreated irrigation water and unconventional organic manure for the production (Samaké et al., 2011; Uyttendaele et al., 2015; Atidégla et al., 2016; Khan et al., 2018; Iwu and Okoh, 2019; Banach  et   al.,  2020).   These   agricultural   inputs   are sometimes sources of parasitic contamination on vegetables (Abe et al., 2016; Ghimire et al., 2020). The accumulation of parasites in soil and the water used to irrigate crops, raises concerns about contamination of the food chain. Literature reported the link between foodborne illness and the consumption of fresh vegetables (Olyaei and Hajivandi, 2013; CallejÓn et al., 2015; Alhabbal, 2016). Contamination is linked to the use of untreated wastewater in vegetable production. Among pathogens causing diseases, intestinal parasitic infection is responsible for infecting more than two billion individuals worldwide (Tigabu et al., 2019). And some species of protozoan parasites could cause serious health problems and economic issues (Yusof, 2017).

Campos et al. (2018) have found helminth eggs in agricultural irrigation water (0.1–3 total helminth eggs/L) in Colombia. In addition, Kafle et al. (2014) obtained eggs of Ascaris lumbricoides, Strongyloides stercoralis and Giardia in vegetables soil in Nepal. Also, studies done by various authors demonstrated the contamination of vegetables by many parasites such as Entamoeba spp. (histolytica, dispar and coli), A. lumbricoides, Giardia lambliae, Trichuris trichura, Fasciola spp., Echonococcus spp., Toxocora spp., S. stercoralis (Alemu et al., 2020; Idahosa, 2011; Sia et al., 2012; Eraky et al., 2014; Mohamed et al., 2016; Rahmati et al., 2017). The use of contaminated soil has been found to be source of parasitic contamination of vegetables (K?ape? and Borecka, 2012; Amoah, 2014). Untreated irrigation water has been reported to be responsible for vegetables contamination in West and East Africa (Cobbina et al., 2013; Amoah, 2014; Akinde et al., 2016; Woldetsadik et al., 2017; Amoah et al., 2018; Kayombo and Mayo, 2018). Untreated irrigation water is used in agriculture because of its advantages, as they are rich in nutrients. It increases yield and reduces production costs by saving fertilizers (Valipour and Singh, 2016; Libutti et al., 2018; Arena et al., 2020; Ungureanu et al., 2020).Literature reported that long-term irrigation with wastewater induces changes in chemical and biological properties of soils. This could present a potential risk of contamination of vegetables by biological and chemical agents (Edokpayi et al., 2016; Alengebawy et al., 2021). Transmission of helminths from the digestive tract is linked to the consumption of raw vegetables exposed to wastewater (Adegoke et al., 2018; Amoah et al., 2018). WHO has reported that lettuce eaten raw, irrigated with untreated sewage could cause transmission of parasitic nematode infections (WHO, 2006).  No study has been done in Mali to determine the parasitic quality of vegetables.The economy of Mali is not strong to support the construction of irrigation channels as recommended by WHO standard (WHO, 2006) and Government cannot also stop farmers from using the water because the livelihoods of many people depend on it. Since the treatment of untreated water is not a realistic option and banning its use will threaten many livelihoods and urban  vegetable  supply in Mali. This study therefore aimed at determining the parasitic contaminants of lettuce, tomato and cucumber from some vegetable production sites in Mali, in order to assess the health risk related to their consumption.


 RESULTS AND DISCUSSION

Study sites

The study was done from June to December 2015 in Bamako (12° 39′ 00″ N, 8° 00′ 00″ W), Kati (12° 45′ 00″ N, 8° 04′ 00″ W), Baguineda (12° 37′ 00″ N, 7° 47′ 00″ W), Samanko (12°32'1" N, 8°5'3" W), Sikasso (11° 19′ 00″ N, 5° 40′ 00″ W) and Niono (14° 15′ 09″ N, 5° 59′ 34″ W). Kati, Baguineda and Samanko are peri-urban areas of Bamako, whilst Sikasso is the third region and Niono is part of the fourth region in Mali. These sites were chosen based on their accessibility and the presence of active farmers. The choice of these sites was also due to the fact that they are bulk vegetables production sites where producers use untreated water for irrigation and undecomposed organic manures for their cultivation. After the selection of sites, farmers who agreed to collaborate were selected for this study.

Sampling

Samples of lettuce, tomato and cucumber were taken randomly from farms irrigated with untreated irrigation water in Bamako, Kati, Baguineda, Samanko, Sikasso and Niono. Six samples each of lettuce, tomato and cucumber were taken randomly per site, for all of the sites (except Bamako, where only lettuce samples were taken) selected for the study. Thirty-six heads of lettuce, thirty tomatoes and cucumbers fruits each were taken from different farms. The various samples were carefully labeled, put in a sterile plastic bag, placed in polythene bags and transported on ice to the laboratory where they were analyzed immediately or stored at 4°C within 24 h before analysis. Lettuce leaves were removed from each head and combined to obtain a composite sample. Each sample of tomato and cucumber was carefully cut using sterile scissors and mixed to obtain a composite sample. Parasitic analysis was performed according to the method of Uga et al. (2009). Helminth eggs population on lettuce leaves, tomato and cucumber surface were determined by washing 100 g of each in one liter of sterile physiological saline solution (0.85% NaCl). The washing solution was allowed to settle for 10 h in one liter flask. The suspension was decanted, and the pellet transferred into 15 ml centrifuge tubes and centrifuged at 2164 rpm for 15 mn. The flask was rinsed three times with distilled water, and the solutions transferred into centrifuge tubes. All pellets contained in different tubes were added together into one tube and centrifuged again for fifteen minutes at 2164 rpm. The suspension was decanted and all deposits were added together into one tube and centrifuged again at the same speed and for the same period. Then, much of the supernatant was removed by micropipette by leaving one millilitre of the pellet. The pellet (for each sample) was observed examined in lugol on a slide under the microscope (x100), and the eggs were counted on three pellets and averaged.


 RESULTS

The composition of parasites  

Lettuce and tomato samples in Bamako, Baguineda, Kati, Samanko  and  Niono  were  contaminated   by  parasites vegetative form and parasites eggs. Between parasites, protozoan like 30 Entamoeba coli and Trichomonas intestinalis had the highest rates with 24.19% each. These were followed by 16.43 A. lumbricoides (13.25%), 16 Giardia intestinalis (12.9%), 14 Balantidium coli (11.29%), 9 Entamoeba histolitica (7.26%), 4 Fasciola hepatica (3.23%), 2 Trichinella spiralis (1.61%), 1.29 Ancylostoma duodenale and Schistosoma intercalatum (1.04% each) (Figure 1).  The host of these parasites are humans, so their presence on lettuce and tomato samples could pose a health risk to population. Lettuce, most vulnerable vegetable to parasites was contaminated by 30 Entamoeba coli, 16 G. intestinalis, 11 B. coli, 5 E. histolitica, 4 F. hepatica, 2 T. spiralis, 1.29 A. duodenale and S. intercalatum. Only 30 T. intestinalis, 3 B. coli and 4 E. histolitica have been found on tomato samples.

Parasite load per site and per vegetable

The parasitic load of lettuce, tomato and  cucumber  were determined in Bamako, Baguineda, Kati, Samanko and Niono. Cucumber samples were free of parasites at all sites and no parasite eggs were found on vegetables from Sikasso. In total, 20 (20.83%) of all vegetable samples were contaminated by parasites eggs, for which 15 (14.40%) lettuce and 5 (4.80%) tomato samples. All the 6 lettuce samples at Bamako were contaminated by parasites; 3 samples of lettuce and 1 of tomato in Kati; 1 sample each of lettuce and tomato in Samanko; 1 lettuce sample in Baguineda; four samples of lettuce and 3 of tomato in Niono. Among vegetables, lettuce was the most contaminated by parasites eggs with a percentage of 41.66, following by tomato (16.66). No parasite was found on cucumber (Figure 2). Lettuce in Bamako and Niono had the highest percentage of contamination (83.33). High percentage of contamination of tomato  (50.00) was obtained in Niono.

Lettuce samples were contaminated with 30 E. coli (30 at Niono), Ascaris lumricoides (16.43 for which 12 at Bamako and 4.43 at Niono), Giardia intestinalis (16 at Baguineda),  B.  coli (11  at  Niono),  E.  histolitica   (5   at Bamako), F. hepatica (4 for which 2 in Bamako and Kati, each), T. spiralis (2 at Bamako), A. duodenale (1.29 at Bamako) and S. intercalatum (1.29 at Kati). Only T. intestinalis (30 at Niono), B. coli (3 at Kati) and E. histolitica (4 for which 2 at Samanko and 2 at Niono) have been found on tomato samples.


 DISCUSSION

In this study, 20.83% of parasitic contamination were obtained amongst all (96) vegetable samples. This is in agreement with the findings of Abougrain et al. (2010) who found 58% of vegetables contamination by helminth eggs and cysts of Giardia spp among 126 samples. Their results and ours are similar in term of the presence of parasites, but different regarding the percentage and type of parasites. Their high rate of contamination (58%) compared to us (20.83%) could be due to the fact that they used standard methods, by which the parasites were clearly identifiable.

Lettuce from Bamako and Niono (with the parasitic prevalence of 83.33% of each) were the most contaminated compared to other sites. This high percentage of contamination in Bamako could be due to the fact that vegetable producers use poor quality water and unconventional compost for their production because of the scarcity of cultivable land (Dia, 2017; Traoré, 2020). This can be the basis of several intestinal diseases caused by parasites (Adegoke et al., 2018; Shah et al., 2019).

However, lettuce, tomato and cucumber from Sikasso were free of parasites eggs. Sikasso is an agricultural area par excellence, farmers have enough land and water source. Also, vegetable farmers receive a lot of training in good agricultural practices (composting methods and the use of irrigation water) and irrigation water and soil may not be contaminated compared to other sites. These could be the reason for the absence of parasite eggs in these samples.

In the present study, parasitic analysis of vegetables showed the presence of E. coli and T. intestinalis (24.19% each), A. lumbricoides (13.25%), G. intestinalis (12.9%), B. coli (11.29%) E. histolitica (7.26%), Fluke (3.23%), and Trichina spp. (1.61%). Helminth eggs of A. duodenale and S. intercalatum (1.04% each) were relatively low. Of three types of vegetables examined, lettuce is the most parasitic-infected vegetable (41.66%), followed by tomato (16.66%) and cucumber (0%). This confirms work done by Amaechi et al. (2016), who found A. lumbricoides, Entamoeba spp., F. hepatica, T. trichura on lettuce and tomato. But, found that 40% of cucumber were contaminated, which is different from this study. This is also in line with the result of (Amoah et al., 2014), who obtained eggs of A. lumbricoides, Hymenolepis diminuta, T. trichura, F. hepatica and Strongyloides larvae in lettuce samples.  This study is however, not  consistent with that done by (Chau et al., 2014) who found eggs of Fasciola spp. (83.33%), Ascaris spp. (85.19%) and Trichuris spp. (64.81%), Clonorchis sinensis (16.67%); Cryptosporidium, Isospora and Cyclospora protozoan oocysts in vegetables.

The contamination of vegetables by parasites eggs in other countries have also been reported in Nigeria (Idahosa, 2011), Egypt (Eraky et al., 2014), Ethiopia (Woldetsadik et al., 2017), Ghana (Amoah et al., 2018), Philippines (Sia, 2012), and Sudan (Mohamed et al., 2016). As in the present study, Ascaris spp. have been the common parasites identified in vegetables from these countries at different rates. Ascaris spp. are soil transmitted helminths and their eggs remain persistent in soils for years (Echazú et al., 2015). This may explain his presence in those vegetables. The reasons for parasitic contamination on vegetables were probably from contaminated fertilizers on soil (Uga et al., 2009; K?ape? and Borecka, 2012), and wastewater (Keraita et al., 2014). The differences observed in the levels of different pathogenic intestinal parasites of fresh vegetables reported in this work and other studies were expected. Several factors such as the use of untreated supplies of sewage and water, manure as a fertilizer for crop production, various agronomic practices, methods used for detection of intestinal parasites, the type and number of samples examined (Park et al., 2015; Adegoke et al., 2016).

Consumption of vegetables particularly raw plays an important role in the transmission of parasitic contaminations (Odeyemi, 2016; Punsawad et al., 2019) and is important source of foodborne epidemics in developing countries. A high incidence of human intestinal parasites has been found in communities that consume raw vegetables, particularly when vegetables are grown on farmland fertilized with untreated human and animal waste (Ishaku et al., 2013). The contamination took place before harvest, through contaminated manure, sewage sludge, untreated irrigation water or runoff water from livestock farms or directly from animals wild and domestic.


 CONCLUSION

Vegetable crops analyzed in this study were contaminated by parasites (up to 20.83%). Vegetables (41.66% of lettuce and 16.66 of tomato) were contaminated with parasites, and the parasite load was higher in Bamako and Niono with a prevalence of 83.33% of each compared to other sites. Cucumber samples were free of parasites at all sites. Contamination of fresh vegetables produced in Mali by pathogenic intestinal parasites could constitute a risk of public health concern. The Malian government should sensitize and assist farmers to treat irrigation water and organic fertilizers for vegetable production.  Sellers  should  wash  their   vegetables  with clean water (and changed water after each use) before displaying them on the table. Consumers should also sanitize vegetables before consumption, particularly those eaten raw.


 CONFLICT OF INTERESTS

The authors have not declared any conflict of interests.


 ACKNOWLEDGEMENT

The authors appreciate the West African Agricultural Productivity Program (WAAPP-2A) for the financial support of this project.



 REFERENCES

Abe EM, Ajah LJ, Ayuba SO, Mogaji H, Ekpo UF (2016). Geohelminths contamination of fruits and vegetables sold in Lafia markets. Annual Research and Review in Biology 11(2):1-8. 
Crossref

 

Abougrain AK, Nahaisi M, Madi NS, Saied MM (2010). Parasitological contamination in salad vegetables in Tripoli-Libya. Food Control 21(5):760-762. 
Crossref

 

Adegoke AA, Amoah ID, Stenström TA, Verbyla ME, Mihelcic JR (2018). Epidemiological evidence and health risks associated with agricultural reuse of partially treated and untreated wastewater: a review. Frontiers in public health 6:337. 
Crossref

 

Adegoke AA, Awolusi, OO, Stenström TA (2016). Organic fertilizers: Public health intricacies. In: Larramendy ML, Soloneski S (Eds.), Organic fertilizers-From basic concepts to applied outcomes. IntechOpen.
Crossref

 

Akinde SB, Sunday AA, Adeyemi FM, Fakayode IB, Oluwajide OO, Adebunmi AA, Oloke JK, Adebooye CO (2016). Microbes in irrigation water and fresh vegetables: potential pathogenic bacteria assessment and implications for food safety. Applied Biosafety 21(2):89-97. 
Crossref

 

Alemu G, Nega M, Alemu M (2020). Parasitic contamination of fruits and vegetables collected from local markets of Bahir Dar city, Northwest Ethiopia. Research and Reports in Tropical Medicine 11:17-25. 
Crossref

 

Alengebawy A, Abdelkhalek ST, Qureshi SR, Wang MQ (2021). Heavy metals and pesticides toxicity in agricultural soil and plants: ecological risks and human health implications. Toxics 9(3):42. 
Crossref

 

Alhabbal AT (2016). The prevalence of parasitic contamination on common sold vegetables in Alqalamoun region. International journal of Pharmaceutical Sciences Review and Research 30(18):94:97.

 

Amaechi EC, Ohaeri CC, Ukpai, OM, Adegbite RA (2016). Prevalence of parasitic contamination of salad vegetables in Ilorin, North Central, Nigeria. Momona Ethiopian. Journal of Science 8(2):136-145. 
Crossref

 

Amoah ID (2014). Helminth infection risk associated with the use of wastewater in urban agriculture in Kumasi, Ghana [Master's thesis, Kwame Nkrumah University of Science and Technology]. KNUSTSpace. 

 

Amoah ID, Adegoke AA, Stenström TA (2018). Soil-transmitted helminth infections associated with wastewater and sludge reuse: a review of current evidence. Tropical medicine and International Health 23(7):692-703. 
Crossref

 

Amoah P, Lente I, Senorpe AH, Abaidoo RC (2014). Quality of vegetables in Ghanaian urban farms and markets. In: Drechsel P, Keraita B(Eds.), Irrigated Urban Vegetable Production in Ghana: Characteristics, Benefits and Risk Mitigation. International Water Management Institute, pp. 89-103.

 

Anand SS, Hawkes C, De Souza RJ, Mente A, Dehghan M, Nugent R, Zulyniak MA, Weis T, Bernstein AM, Krauss RM, Kromhout D (2015). Food consumption and its impact on cardiovascular disease: importance of solutions focused on the globalized food system: a report from the workshop convened by the world heart federation. Journal of the American College and Cardiology 66(14):1590-1614. 
Crossref

 

Arena C, Genco M, Mazzola MR (2020). Environmental benefits and economical sustainability of urban wastewater reuse for irrigation: a cost-benefit analysis of an existing reuse project in Puglia, Italy. Water 12:2926. 
Crossref

 

Atidégla SC, Huat J, Agbossou EK, Saint-Macary H, Kakai RG (2016). Vegetable contamination by the fecal bacteria of poultry manure: case study of gardening sites in Southern Benin. International Journal of Food Science 2016:e4767453. 
Crossref

 

Aune D, Giovannucci E, Boffetta P, Fadnes LT, Keum N, Norat T, Greenwood DC, Riboli E, Vatten LJ, Tonstad S (2017). Fruit and vegetable intake and the risk of cardiovascular disease, total cancer and all-cause mortality: a systematic review and dose-response meta-analysis of prospective studies. International Journal of Epidemiology pp. 1029-1056. 
Crossref

 

Banach JL, van der Fels- Klerx HJ (2020). Microbiological reduction strategies of irrigation water for fresh produce. Journal of Food Protection 83(6):1072-1087. 
Crossref

 

CallejÓn RM, Rodríguez-Naranjo MI, Ubeda C, Hornedo-Ortega R, Garcia-Parrilla MC, Troncoso AM (2015). Reported foodborne outbreaks due to fresh produce in the United States and European Union: trends and causes. Foodborne Pathogens and disease 12(1):32-38. 
Crossref

 

Campos MC, Beltrán M, Fuentes N, Moreno G (2018). Helminth eggs as parasitic indicators of fecal contamination in agricultural irrigation water, biosolids, soils and pastures. Biomedica:revista del Instituto Nacional de Salud 38(1):42-53.

 

Chau HLQ, Thong HT, Chao NV, Hung PHS, Hai VV, An LV, Fujieda A, Ueru T, Akamatsu M (2014). Microbial and parasitic contamination on fresh vegetables sold in traditional markets in Hue city, Vietnam. Journal of Food and Nutrition Research 2(12):959-964. 
Crossref

 

Cobbina SJ, Kotochi MC, Korese JK, Akrong MO (2013). Microbial contamination in vegetables the farm gate due to irrigation with wastewater in the Tamale Metropolis of Northern Ghana. Journal of Environmental Protection 4(7):676-682. 
Crossref

 

Dia S. (2017). Contrôle de la qualité bactériologique et toxicologique de la laitue vendue en commune I du District de Bamako, Mali [Unpublished Master's thesis]. Université des Sciences, des Techniques et des Technologies de Bamako.

 

Echazú A, Bonanno D, Juarez M, Cajal, SP, Heredia V, Caropresi S, Cimino RO, Caro N, Vargas PA, Paredes G, Krolewiecki, AJ (2015). Effect of poor access to water and sanitation as risk factors for soil-transmitted helminth infection: selectiveness by the infective route. PLoS neglected tropical Diseases 9(9):e0004111.
Crossref

 

Edokpayi JN, Odiyo JO, Durowoju, OS (2016). Impact of wastewater on surface water quality in developing countries: a case study of South Africa. In: Tutu H (Eds.), Water Quality. IntechOpen.

 

Eraky, MA, Rashed, SM, Nasr, M, El-Hamshary, AM, El-Ghannam AS (2014). Parasitic contamination of commonly consumed fresh leafy vegetables in Benha, Egypt. Journal of Parasitology Research 613960. 
Crossref

 

Ghimire A, Upadhyaya J, Nayaju T, Lekhak B, Chaudhary DK, Raghavan V, Pant BR, Bajgai TR, Koirala N, Upreti MK (2020). Microbial and parasitic contamination of fresh raw vegetable samples and detection of the BlaTEM and BlaCTX-M Genes from E. coli isolates. Agriculture 10(8):341.
Crossref

 

Idahosa OT (2011). Parasitic contamination of fresh vegetables sold in Jos markets. Global Journal of Medical Research, 11(1):20-25.

 

Ishaku AA, Asheofo D, Habibu T, Sunday TM, Amuta EA, Azua AT (2013). Prevalence of intestinal parasitic infections among food vendors in Lafia Metropolis of Nasarawa State, Nigeria. Journals of Biotechnology 2(2):21-25.

 

Iwu CD, Okoh AI (2019). Preharvest transmission routes of fresh produce associated bacterial pathogens with outbreak potentials: a review. International Journal of Environmental Research and Public Health, 16(22):4407. 
Crossref

 

Kafle CM, Ghimire S, Dhakal P, Shrestha U, Poudel KCR., Adhikari N, Tuladhar R (2014). Identification of parasites in soil samples of vegetable field of Bhaktapur District. Tribhuvan University Journal of Microbiology 2(1):26-28.

 

Kayombo MC, Mayo AW (2018). Assessment of microbial quality of vegetables irrigated with polluted waters in Dar es Salaam City, Tanzania. Environment and Ecology Research 6(4):229-239. 
Crossref

 

Keraita B, Silverman A, Amoah P, Senorpe AH (2014). Quality of irrigation water used for urban vegetable production. In Dreschel P, Keraita B (Eds.), Irrigated urban vegetable production in Ghana: characteristics, benefits and risk mitigation. International Water Management Instiute. pp. 89-103.

 

Khan MN, Mobin M, Abbas ZK, Alamri SA (2018) Fertilizers and their contaminants in soils, surface and groundwater. In DellaSala DA and Goldstein MI (Eds.), The Encyclopedia of the Anthropocene. Elsevier Incorporation. pp. 225-240.
Crossref

 

K?ape? T, Borecka A (2012). Contamination of vegetables, fruits and soil with geohelmints eggs on organic farms in Poland. Annals of agricultural and environmental medicine 19(3):421-425.

 

Libutti A, Gatta G, Gagliardi A, Vergine P, Pollice A, Beneduce, L, Disciglio G, Tarantino E (2018). Agro-industrial wastewater reuse for irrigation of a vegetable crop succession under Mediterranean conditions. Agricultural Water Management 196:1-14. 
Crossref

 

Mohamed MA, Siddig EE, Elaagip AH, Edris AMM, Nasr AA (2016). Parasitic contamination of fresh vegetables sold at central markets in Khartoum state, Sudan. Annals of Clinical Microbiology and Antimicrobials, 15:17. 
Crossref

 

Odeyemi OA (2016). Public health implications of microbial food safety and foodborne diseases in developing countries. Food and nutrition research, 60:29819. 
Crossref

 

Olyaei A, Hajivandi L (2013). Parasitological contamination of markets and farms in vegetables consumed in Southern Iran. Global Veterinaria 10:327-331.

 

Park S, Navratil S, Gregory A, Bauer A, Srinath I, Szonyi B, Nightingale K, Anciso J, Jun M, Han D, Lawhon S, Ivanek R (2015). Multifactorial effects of ambient temperature, precipitation, farm management, and environmental factors determine the level of generic Escherichia coli contamination on preharvested Spinach. Applied and Environmental Microbiology 81(7):2635-2650. 
Crossref

 

Punsawad C, Phasuk N, Thongtup K, Nagavirochana S, Viriyavejakul P (2019). Prevalence of parasitic contamination of raw vegetables in Nakhon Si Thammarat province, southern Thailand. BMC Public Health 19:34. 
Crossref

 

Rahmati K, Fallah M, Maghsood AH, Shamsi-Ehsan T, Matini M (2017). The prevalence of parasitic contamination of vegetables consumed in Malayer city, West of Iran, in 2014. Avicenna journal Clinical Microbiology and Infection 4(2):e42380. 
Crossref

 

Samaké F, Babana AH, Yaro F, Cissé D, Traoré I, Kanté, F, Koné S, Diallo S, Touré O, Sako M, Iknane A G (2011). Risques sanitaires liés à la consommation des produits maraîchers cultivés dans la zone urbaine et périurbaine de Bamako. Mali Santé Publique 1(001), 27-31.

 

Shah HA, Huxley P, Elmes J, Murray KA (2019). Agricultural land-uses consistently exacerbate infectious disease risks in Southeast Asia. Nature Communications 10:4299. 
Crossref

 

Sia Su GL, Mariano CMR, Matti NSA, Ramos GB (2012). Assessing parasitic infestation of vegetables in selected market in Metro Manila, Philippines. Asian Pacific Journal of Tropical Disease, pp. 51-54.
Crossref

 

Tigabu A, Taye S, Aynalem M, Adane K (2019). Prevalence and associated factors of intestinal parasitic infections among patients attending Shahura Health Center, Northwest Ethiopia. BMC Research Notes 12:333. 
Crossref

 

Traoré S (2020). Microbial and chemical contamination of irrigated lettuce (Lactuca sativa L.) in some urban and peri-urban areas in Mali. [Unpublished doctoral dissertation]. University of Ghana.

 

Uga S, Hoa NTV, Noda S, Moji K, Cong L, Aoki Y, Rai SK, Fujimaki Y (2009). Parasite egg contamination of vegetables from a suburban market in Hanoi, Vietnam. Nepal Medical College Journal 11(2):75-78.

 

Ungureanu N, Vl?dut V, Voicu G (2020). Water scarcity and wastewater reuse in crop irrigation. Sustainability 12:9055. 
Crossref

 

Uyttendaele M, Jaykus LA, Amoah P, Chiodini A, Cunliffe D, Jacxsens L, Holvoet K, Korsten L, Lau M, McClure P, Medema G, Sampers I, Jasti PR. (2015). Microbial hazards in irrigation water: standards, norms, and testing to manage use of water in fresh produce primary production. Comprehensive Reviews in Food Science and Food Safety 14(4), 336-356.
Crossref

 

Valipour M, Singh, VP (2016) Global experiences on wastewater irrigation: Challenges and prospects. In. Maheshwari B, Thoradeniya B, Singh VP (Eds.), Balanced Urban Development: Options and Strategies for Liveable Cities: An epilogue. Springer Cham. pp. 289-327.
Crossref

 

WHO (World Health Organization), (2006). WHO guidelines for the safe use of wastewater, excreta and greywater use in agriculture.

View

 

Woldetsadik D, Drechsel P, Keraita B, Itanna F, Erko B, Gebrekidan H (2017). Microbiological quality of lettuce (Lactuca sativa) irrigated with wastewater in Addis Ababa, Ethiopia and effect of green salads washing methods. International Journal of Food Contamination 4(3). 
Crossref

 

Yusof AM, Mohammad M, Abdullahi MA, Mohamed Z, Zakaria R (2017). Occurrence of intestinal parasitic contamination in select consumed local raw vegetables and fruits in Kuantan, Pahang. Tropical Life Sciences Reseach 28(1):23-32.
Crossref

 




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