Effect of garri processing effluents [waste water] on the cyanide level of some root tubers commonly consumed in the South East of Nigeria.
The deleterious effects of cyanide, even at low concentrations have been widely reported [1, 2]. The lethal dose of hydrocyanic acid [HCN] taken by mouth is 0.5-3.3 mg/kg body weight [3, 4]. There are continuing efforts to further reduce the cyanide levels in plant foods through the production of better cultivars and food processing techniques [5, 6, 7]. Under normal physiological conditions, tissues of cyanophoric plants do not contain free cyanide; rather they contain cyanogenic glycosides, which upon hydrolysis by endogenous glycosidase yield free cyanide which could be toxic to the consumer [8, 9]. The sources of cyanide found in soil are from disposal of cyanide wastes in landfills, and use of cyanide-containing road salts. Cyanide exists as free and bound cyanide. The free cyanide [HCN] is not found in healthy growing plants, but develops when normal growth has been retarded by drought or other adverse conditions . Plants can also take up cyanide from soils polluted by organic salts containing cyanide ion [CN-] or cyanides from industrial waste . During the process of producing cassava starch from (Manihot esculenta) roots, large amounts of cyanoglycosides are released, which rapidly decay to [CN.sup.-] following enzymatic hydrolysis. Depending on the varying cyanoglycoside content of the cassava varieties, the cyanide concentration in the wastewater is as high as 200 mg/l. .
Ingestion of cyanide containing staple foods such as cassava and forage plants have accounted for many instances of cyanide poisoning in humans and animals . Cyanide is a highly toxic element and has been implicated as a causative agent in certain diseases such as Leber's optical atrophy, tobacco amblyopia, Tropical Ataxic Neuropathy [TAN], endemic goiter and cretinism syndrome . The most important effect of cyanide is the inhibition of tissue respiration . A number of enzymes like catalase, superoxide dismutase, nitrate reductase are inhibited by cyanide, as well as a number of metalloenzymes like alkaline phosphatase, cytosolic Cu/Zn superoxide dismutase [12,14].The cyanide ion or radical [CN-] is the strong poison and is rapidly absorbed from the gastrointestinal tract [GIT]. The actual toxicity depends on the rate of absorption and the ability of the body to dispose of the cyanide . Cyanide concentration of less than 50mg/kg in food is slightly poisonous; 80-100mg/kg is toxic, while levels above 100mg/kg are fatal; and lethal dose of cyanide in adult humans is of the order of 50-60mg/kg [1, 16]. The WHO recommended safe level is 10mg of HCN/kg body weight .
Roots and tubers are thickened underground starch storage organs of some plants. Except for cereals, tubers crops are the most important groups of staple foods in the world [18, 19]. Though important as they may be, tuber crops have hitherto received scanty attention from researchers. Research has been mostly on cash crops, since tubers yield less acceptable industrially processed products. Recently, however, the situation is changing because the quality and quantity of tuber crops have been improved through increased research stimulated by largescale starvation and population explosion . The principal tuber crops of economic importance in Nigeria include Dioscorea rotundata (white yam), Dioscorea alata (water yam), Xanthosoma sagittifolium (white cocoyam), Colocasia esculenta (red cocoyam), Manihot esculenta (cassava), Ipomea batatas (red sweet potato), Ipomea batatas (white sweet potato) and the Dioscorea dumetorum (domestic and wild trifoliate yam) .
These tubers are consumed processed in various forms, cooked, boiled, and fried. There are reports of sudden death from consumption of these tubers . It has also been reported [1, 3, 15], that cyanide levels of plants vary according to the environments where they grow.
Hence, it was found necessary to assay for the cyanide levels in some root tubers grown in a cassava processing plant effluent [waste water] contaminated farm land and commonly consumed in South East of Nigeria.
MATERIALS AND METHODS
The study area was Umuariaga town in Ikwuano Local Government Area of Abia State Nigeria. The area is popular and known for cassava production all year round, which is readily processed into garri flour. The effluent (waste water) from the "processed" milled cassava is allowed to flow into farmlands where the processing plants are located.
Healthy root tuber samples identified and authenticated were collected from the herbarium of the National Roots Crops Research Institute (NRCRI), Umudike.
The tubers were planted on the 1st of April 2010 on both the waste water contaminated site and control (none contaminated) site, and harvested on the 30th day of December, 2010. Planting was done in rows of fours and 64m apart. This spacing was to achieve equal nutrient availability for the tubers.
Extraction and Determination of cyanide:
The samples were washed with distilled water and then ground into a paste in a mortar and used for wet (fresh) analysis. The sample paste (15g) was weighed into a 1000ml flask and 200ml distilled water was added and allowed to stand for 4hr. The resulting mixture was then vacuum- distilled and the distillate collected in 20ml of NaOH solution, as described by AOAC .
The HCN contents of the samples were determined using the alkaline titration method of Association of Official Analytical Chemists .The distillate was diluted to 250ml and an aliquot of 100ml was titrated by adding 8ml of 6N NH4OH solution and 2ml of 5% KI solution. This was then titrated against 0.02N AgNO3 solution to get a light turbid end point. The titer values were then used to calculate the cyanide concentrations in mgHCN/kg.
[1ml of 0.02N AgN[O.sub.3] = 1.08mgHCN].
Values are represented as mean [+ or -] SEM. Data were analyzed using one-way analysis of variance (ANOVA) followed by Fisher LSD test at 5%. Differences between test and control were considered significant for p<0.05.
Table 1 shows the cyanide levels of the root tubers for the cassava processing plant effluent site and the control site. For D dumetorum (domestic), cyanide level at the effluent (waste water) site is 35.49 [+ or -] 1.69mgHCN/kg, which is significantly (p<0.05) higher than the control site sample value of 32.76 [+ or -] 0.51mgHCN/kg. Cyanide level of D. dumetorum (wild) 43.88 [+ or -] 2.39mgHCN/kg was also significantly (p<0.05) higher than 41.06 [+ or -] 0.94mgHCN/kg at the control site. At the effluent contaminated site D. rotundata cyanide content was 10.13 [+ or -] 1.90mgHCN/kg which was not significant at (p<0.05) compared to 9.65 [+ or -] 1.36mgHCN/kg for samples from the control site. There is also significant difference (p<0.05) in cyanide levels of D. alata samples from control and effluent contaminated sites 9.12 [+ or -] 0.93 and 8.45 [+ or -] 1.60mgHCN/kg respectively. X.sagittifolium and C. esculenta have significantly (p<0.05) higher cyanide concentrations at the cassava effluent site compared to the control 15.19 [+ or -] 1.61 and 11.81 [+ or -] 1.19mgHCN/kg compared to 14.77 [+ or -] 1.13 and 10.89 [+ or -] 1.55mgHCN/kg respectively. There are no significant differences at p<0.05 for I.batatas (red) cyanide levels for both sites: 6.75 [+ or -] 1.19 and 6.13 [+ or -] 0.70mgHCN/kg, respectively, while I. batatas (white) cyanide level 8.44 [+ or -] 1.20mgHCN/kg for waste water contaminated site is significantly (p<0.05) higher than 7.26 [+ or -] 1.34mgHCN/kg for samples from the control site.
The higher cyanide levels of the root tuber samples from the waste water contaminated site shows that the cyanide levels of the tubers may have been influenced by the effluent (waste water) from the cassava processing plant. Cyanide occurs naturally in a variety of fruits, vegetables and grains, while some plants also absorb cyanide from the soil . Padmaja  and Onabolu et al.  reported that cyanide can be found in most plants in the form of cyanogenic glycoside. Ingestion of cyanide containing staple foods such as cassava and forage plants have accounted for many instances of cyanide poisoning in humans and animals. The exposure of persons to gaseous cyanide leading to intoxication by inhalation causes acute cyanide poisoning, while dietary exposure may occur as a result of high intake of the products of some nutritive plants of different root tubers; which contain cyanogenic glycosides [4,2]. On hydrolysis, these cyanogenic glycosides liberate hydrogen cyanide. Eating some foods like almonds, apricots, peach pits, root tubers are various means through which man gets exposed to cyanide.
Jorgensen  reported that plants that are grown in soil with low potassium content or high nitrogen have high hydrocyanic acid concentration in their tubers; and also as the plants get older, the hydrocyanic acid content of the tubers increases, attains a peak and then begins to decline. The ingestion of cyanide or a cyanogenic glycoside can trigger off a lot of toxic manifestations. Ingestion of acute and innocuous levels of cyanide is known to cause instant death and a number of debilitating neurological disorders, respectively [3, 4]. Following ingestion of cyanogenic glycosides; cyanide ions are rapidly absorbed from the gastro-intestinal tract (GIT). Several cases of cyanide poisoning have been reported in humans and animals. Cyanide intake from cassava dominated diet has been proposed as a contributing factor in two forms of nutritional neuropathies; Tropical Ataxic Neuropathy (TAN) described from Nigeria and Epidemic Spastic Paraparesis (ESP) described from Mozambique . The clinical picture of these diseases was dominated by damage to one of the sensory tracts in the spinal cord resulting in an uncoordinated gait called ataxia . A strong association between Epidemic Spastic Paraparasis (ESP) and high dietary intake of cyanide and low intake of sulphur needed for cyanide detoxification has been confirmed . Cassava diets poor in iodine have also been implicated in high incidence of endemic goiter in areas of high consumption .
Also cyanide exposure which interferes with iodine metabolism is a possible cause of spinal cord damage . Repeated oral ingestion of sub-lethal doses of cyanide can also lead to chronic neurological problems, as two neurological syndromes resulting from chronic exposure to cyanide have been identified in humans. These are Lebers' disease and tobacco amblyopia which are caused by hydrocyanic acid contained in tobacco smoke . In animals, the symptoms of hydrocyanic acid poisoning are increases in rate and depth of respiration, increased pulse rate, no response to stimuli and spasmodic muscular movements. It is also reported that the most common characteristics of cyanide poisoning in animals are dark muscle tissue, congestion or hemorrhage of the lungs, patechination of the tracheal mucosa and a frothy bloody damage from the mouth and nostrils . In man, the sequence of events in acute poisoning are hyperventilation, headache, collapse and coma, nausea and vomiting, generalized weakness, perhaps with convulsion and then respiratory depression. With large doses, collapse, coma and death may occur . Cyanide, carbon monoxide, hydrogen sulphide and azide effectively inhibit cytochrome oxidase. They prevent the mitochondrial oxidation as well as phosphorylation. ATP synthesis (phosphorylation) is dependent on electron transport. Hence inhibitors of electron transport chain also inhibit ATP formation. These compounds inhibit electron transport in cells in which such transport is coupled with ATP-synthesis, but they do not affect electron transport in cells in which transport is not coupled with phosphorylation
Observations also show that plants can also take up cyanide from soils polluted by organic salts containing cyanide ion [[CN.sup.-]] or cyanides from industrial wastes as reported by El-Sharkang . The cyanide levels of these root tubers may not pose any considerable danger to consumers since their average cyanide content is still below the estimated maximum sub-lethal dose of 20mgHCN/kg . Also the processing methods: cooking, frying, boiling may further decrease these cyanide levels.
Other factors that may influence the cyanide levels of these root tubers include the soil type, since different soil types would retain cyanide to a varying degree. The age of the processing plant and by extension the age of the cassava waste water effluent and the specie of the cassava that is most processed would also influence the cyanide content of these root tubers.
This study, therefore, has provided results that show some root tubers grown on a cassava effluent waste water) contaminated soil could have their cyanide contents increased.
This speculation thus raises concern for people who may end up amassing toxic levels of cyanide from chronic low-level intake from these root tubers. Further investigations into the level of exposure of consumers and the systemic bioavailability of the cyanide upon consumption of the tubers and the short and long term toxicological implications and impact on consumers' health are recommended among the population.
In conclusion, though cyanide is sparingly soluble in water and can be drastically reduced during cooking of these tubers, the fact still remains that if the tubers are not properly processed, consumers may be exposed to lethal dose levels of cyanide which may be unsafe and could cause acute poisoning if not instant death. It is therefore recommended, proper disposal methods for garri processing effluents and discourage the planting of tubers and crops on lands contaminated by the effluents.
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Uhegbu FO (1) *, Akubugwo EI (1) and EEJ Iweala (2)
* Corresponding author email: firstname.lastname@example.org
(1) Department of Biochemistry, Abia State University, PMB 2000, Uturu, Nigeria.
(2) Department of Biological Sciences, Covenant University, Ota, Nigeria.
Table 1: Cyanide levels of root tubers (mgHCN/kg) Sample Common Names Control site Dioscorea dumetorum Domestic yam 32.76 [+ or -] 0.05 * Dioscorea dumetorum Wild yam 41.06 [+ or -] 0.94 * Dioscorea rotundata White yam 9.65 [+ or -] 1.36 Dioscorea alata Water yam 8.45 [+ or -] 1.60 * Xanthosoma Cocoyam 14.77 [+ or -] 1.33 * sagittifolium (red) Colocasis esculenta Cocoyam 10.89 [+ or -] 1.55 * (white) Ipomea batatas Sweet potato 6.13 [+ or -] 0.70 (red) Ipomea batatas Sweet potato 7.26 [+ or -] 1.34 * (white) Sample Waste water site Dioscorea dumetorum 35.49 [+ or -] 1.69 * Dioscorea dumetorum 43.88 [+ or -] 2.39 * Dioscorea rotundata 10.13 [+ or -] 1.90 Dioscorea alata 9.12 [+ or -] 0.93 * Xanthosoma 15.19 [+ or -] 1.61 * sagittifolium (red) Colocasis esculenta 11.81 [+ or -] 1.19 * (white) Ipomea batatas 6.75 [+ or -] 1.19 (red) Ipomea batatas 8.44 [+ or -] 1.20 * (white) Values are mean [+ or -] SD of triplicate determinations. Values with asterix vary significantly
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|Author:||Uhegbu, Friday Obinwa; Akubugwo, E.I.; Iweala, E.E.J.|
|Publication:||African Journal of Food, Agriculture, Nutrition and Development|
|Date:||Oct 1, 2012|
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