Time Impact on Spatio -Temporal Density of Microbial Air Contaminants in the Dewatering Zone of Smallholder Gari Processing Facility in the Niger Delta Region of Nigeria Volume 4 - Issue 5

Enetimi Idah Seiyaboh¹, Glory Richard² and Sylvester Chibueze Izah³*

• ¹Department of Biological Sciences, Niger Delta University, Nigeria
• ²Department of Community Medicine, Niger Delta University, Nigeria
• ³Department of Biology, Bayelsa Medical University, Nigeria

Received: February 24, 2020;   Published: March 10, 2020

Corresponding author: Sylvester Chibueze Izah, Department of Biology Bayelsa Medical University, Nigeria

DOI: 10.32474/OAJESS.2020.04.000198

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Abstract

This study investigated the time impact of spatio -temporal microbial density of air contaminants in the dewatering zone of smallholder gari processing facility in the Niger Delta region of Nigeria. Triplicate petri dishes containing solidified Nutrient Agar, Saboraud Agar and MacConkey agar were exposed for 30, 40 and 50 minutes within 2-meter radius of the facility at the dewatering stage of gari processing at a height of 2.5 feet above ground. The agar plates were incubated, and the resulting microbial density determined. Results showed that the density of the microbes were in the range of 11.67 -34.67cfu/30 minutes, 22.00 -53.00cfu/40 minutes and 55.67 -84.67cfu/50 minutes, for total heterotrophic bacteria; 8.00 -24.33cfu/30 minutes, 10.33 -37.00 cfu/40 minutes and 18.67 -55.00cfu/50 minutes, for total fungi, and 7.00 -22.67cfu/30 minutes, 18.00 -34.00cfu/40 minutes and 30.00 -43.67cfu/50 minutes, for enterobacteriaceae counts. Statistically, there were significant variations (p<0.05) across the locations and time. The occurrence of bacteria from the enterobacteriaceae family may have stemmed from the fact that domestic animals such as goats, fowls and even rats move freely within the mills in search of food. The overall high density of microbes is attributable to the exposure time in the dewatering phase of gari processing. The researchers concluded that vulnerable individuals (immunosuppressed\ or compromised, children and elderly) may be susceptible certain disease conditions through bioaerosol inhalation.

Keywords: Bioaerosol, Cassava processing, Environmental contaminants, Public health

Introduction

Air is an integral part of the components of the environment. Air pollutants majorly emanate from human activities and to a lesser extent from natural processes. Air pollutants have the tendency to alter the biotic constituents of an ecosystem which impact on the flora and fauna of the ecosystem in a manner peculiar to the toxicity of the pollutants. Meteorological indicators such as wind speed and direction, temperature etc. may have an effect on the dispersal and absorption rate of air pollutants. In addition, exposure duration may have an effect on the toxicity of air pollutants. Microorganisms are found in diverse environments including soil, sediments, water, and air. The ubiquitous presence of microbes is a major concern in hospitals, food processing units and other sectors where sterility is required, prompting strict control measures aimed at eradicating or minimizing their presence. Authors have defined bio-aerosols as airborne particulate containing living organisms such as microbes or originating from living organisms, such as metabolites, toxins or fragments of microorganisms [1-4]. As such bio-aerosols are obtained in several environmental conditions including waste dumpsites, processing units among others.
Cassava processing into gari is among the major sources of livelihood of several families in southern Nigeria. Gari production is mostly carried out by smallholders using rudimentary equipment. Gari is produced with the following steps: peeling, washing off of debris, grating, bagging, dewatering/ pressing, sieving and frying [5,6]. During dewatering/ pressing large amounts of wastewater often called cassava mill effluents are generated [6-8]. In the environment, the effluent often decomposes through the activities of indigenous microbes [6,9]. During this process offensive odors are perceived few distances away from the dewatering zone. In addition, the effluents have shown to alter the physicochemical and biological characteristics of the receiving soil [10].

Authors have identified Staphylococcus aureus, Escherichia coli, Pseudomonas aerugionsa, Bacillus, Micrococcus, Klebsiella, Streptococcus, Chromobacterium, Proteus, Enterobacter, Aspergillus, Penicillium, Mucor, Rhizopus species and Saccharomyces cerevisiae in cassava mill effluent contaminated soil [10-14] Some species of these microbes have been reported to cause diseases in animals and humans especially immune- compromised individuals. In addition, some of these microbes may likely be the microbes found in gari processing facilities. Again, authors have reported Escherichia coli, Staphylococcus aureus, Micrococcus, Staphylococcus, Streptococcus, Pseudomona, Klebsiella and Bacillus species, and Absidia, Alternaria, Cladosporium, Fusarium, Aspergillus, Geotrichum, Mucor, Penicillium, Phoma, Rhizopus, Curvularia species and Candida albicans as microbial bio-aerosol found in waste dumpsite in some regions in southern Nigeria [3,15].
The vast presence of microbes and the crucial role they play in public health issues, has necessitated this study focusing on the microbial density of air contaminants in the dewatering zone of smallholder gari processing facility in the Niger Delta region of Nigeria.

Materials and Methods

Study Area

This study was carried out in a smallholder cassava grating mill in the Niger Delta region of Nigeria. Gari production from cassava tubers is carried out using rudimentary equipment. Cassava farming and processing together with other food crops such as yam, maize etc. is the main source of livelihood to the upland people of the Niger Delta. The climate of the area is similar to other Niger Delta areas with relative humidity and temperature within 50 -95% and 28 ±8 °C, respectively all year round [6,7,16]. Two major seasons (viz: wet and dry) occur in the area.

Field Sampling and Analysis

Microbial density was determined using sedimentation method. The media was prepared and labelled accordingly as Nutrient agar (for the enumeration of total heterotrophic bacteria), Saboraud dextrose agar (for the enumeration of total fungi) and MacConkey’s Agar for the enumeration of bacteria belonging to the enterobacteriaceae family. The agar was prepared according to the manufacturers guide and it contained approximately 20mls of prepared agar. Triplicate petri dishes containing the solidified agars were exposed for 30, 40 and 50 minutes at the dewatering area of the cassava processing mills/ Locations. Stations A, B, C, D, E (experiment) and station F (control) where established at a suspended height of 2.5 feet. Thereafter, the exposed agar plates were incubated at room temperature for 24 -48 hours for bacteria and 4 -5 days for fungi. The density of the microbes was determined according to the [17,18].

Statistical Analysis

Statistical Package for Social Sciences was used to carry out the statistical analysis. The data was expressed as mean± standard deviation. One way-analysis of variance was used to show significant deviation at P=0.05 across the locations, and Waller - Duncan statistics was used to discern the source of disparity.

Results and Discussion

Spatio-temporal and time effects on the bioaerosol density in the dewatering zone of smallholder gari production from cassava tuber in the Niger Delta region of Nigeria are presented in Table 1. The density of the total heterotrophic bacteria counts at Locations A, B, C, D, E and F were 11.67±2.25 cfu/30 minutes, 22.00±2.65 cfu/30 minutes, 21.33±3.51 cfu/30 minutes, 34.67±3.06 cfu/30 minutes, 41.00±6.25 cfu/30 minutes and 6.00±3.00 cfu/30 minutes, respectively for 30 minutes exposure time interval, 22.00±7.00 cfu/40 minutes, 36.67±4.62 cfu/40 minutes, 36.67±9.87 cfu/40 minutes, 46.67±4.51 cfu/40 minutes, 53.00±3.61 cfu/40 minutes and 7.00±2.00 cfu/40 minutes, respectively for 40 minutes exposure time interval, and 55.67±15.53 cfu/50 minutes, 65.67±22.03 cfu/50 minutes, 71.67±15.04 cfu/50 minutes, 69.33±6.51 cfu/50 minutes, 84.67±7.64 cfu/50 minutes and 7.67±2.08 cfu/50 minutes, respectively for 50 minutes exposure time interval. Statistically, there were significant discrepancies (p<0.05) across the locations and time. In each of the locations, there was an increase in the density of the total heterotrophic bacteria counts as the exposure time interval increased (Figure 1), though statistically significant across some locations.

The density of the total fungi counts at Locations A, B, C, D, E and F were 8.00±1.00cfu/30 minutes, 15.67±3.51 cfu/30 minutes, 23.00±5.57 cfu/30 minutes, 24.33±5.03 cfu/30 minutes, 28.33±1.53 cfu/30 minutes and 4.00±2.00 cfu/30 minutes, respectively for 30 minutes exposure time interval, 10.33±1.53 cfu/40 minutes, 27.00±3.00 cfu/40 minutes, 29.00±3.46 cfu/40 minutes, 35.67±9.61 cfu/40 minutes, 37.00±4.58 cfu/40 minutes and 4.00±1.00 cfu/40 minutes, respectively for 40 minutes exposure time interval, and 18.67±4.51 cfu/50 minutes, 36.67±4.62 cfu/50 minutes, 49.67±7.64 cfu/50 minutes, 49.33±4.16 cfu/50 minutes, 55.00±10.58 cfu/50 minutes and 5.00±3.61 cfu/50 minutes, respectively for 50 minutes exposure time interval. There were significant discrepancies (p<0.05) across the locations and time. For each of the locations, the total fungi count increased with an increase in exposure time interval (Figure 2), which was significant for some Locations as shown by post hoc test (Table 1).
The density of the enterobacteriaceae counts at Locations A, B, C, D, E and F were 7.00±2.65 cfu/30 minutes, 15.67±1.53 cfu/30 minutes, 19.33±1.53cfu/30 minutes, 22.67±4.93 cfu/30 minutes, 21.33±3.51 cfu/30 minutes and 3.67±2.52 cfu/30 minutes, respectively for 30 minutes exposure time interval, 18.00±5.00 cfu/40 minutes, 18.33±1.53 cfu/40 minutes, 29.00±6.25 cfu/40 minutes, 34.33±9.71 cfu/40 minutes, 30.00±2.00 cfu/40 minutes and 3.00±2.00 cfu/40 minutes, respectively for 40 minutes exposure time interval, and 30.00±3.61 cfu/50 minutes, 28.33±4.04 cfu/50 minutes, 38.67±3.06 cfu/50 minutes, 42.67±8.50 cfu/50 minutes, 42.67±4.51 cfu/50 minutes and 5.67±4.62 cfu/50 minutes, respectively for 50 minutes exposure time interval. There were significant discrepancies (p<0.05) across the locations and time. A significant increase exists as the exposure time interval increases for most of the locations in addition to the apparent elevation in the density of the enterobacteriaceae counts that occurred as exposure increased (Figure 3).

This study showed that there is significant dissimilarity across the locations. This may be due to the fact that some of the mills are located close to dumpsites also other anthropogenic activities close to the dewatering area may have contributed to the variation in the microbial density across the locations. Climatic factors such as wind speed and direction during sampling may also a role in the observed deviation for each of the locations. In a related study, Angaye et al. [19] reported higher total heterotrophic bacteria (49-73cfu/50 minutes) in dry season in contrast with the value (44-51cfu/30 minute) in wet season from waste dumpsite in the Niger Delta region of Nigeria. The authors further reported total fungi and enterobacteriaceae as 24-37 and 22-43 cfu/50 minutes, respectively in dry season, and 17-37cfu/50 minutes and 20-31 cfu/50 minutes, respectively in wet season. Across the stations, station F (control) had the least microbial density for each of the microbial groups (total heterotrophic bacteria, total fungi and Enterobacteriaceae counts) measured implicating dewatering as a possible reason for the increased microbial density at gari processing facilities particularly in the study area. The presence of microbial population in the control could be due to the ubiquitous nature of most microorganisms. This study also showed that as the exposure duration increased, the density of each group of microbes under study increased. Again, this suggests the effect of time on the microbial density of the air within the dewatering unit during cassava processing to gari. The occurrence of Enterobacteriaceae counts may be associated with fecal coliforms present in the vicinity of the study area arising from domestic animals such as goats and fowls which often move freely within the vicinity of the mills in search of food.

Conclusion

Gari production by small scale processors in the Niger Delta is carried out using rudimentary equipment. Cassava production and processing into different products is among the sources of livelihood to several families especially those ones in the upland region. This study evaluated the time related spatio - temporal impact of the density of microbial air contaminants from the dewatering stage of gari processing. This study also showed that microbial air contaminants arising from the dewatering stage of gari production by smallholder processor tends to differ from one mill to another and also dependent on duration of exposure.

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