Electronic waste (e-waste) includes an increasing range of electronic appliances from large household appliances, such as refrigerators, air-conditioners, cell phones, stereo systems and consumable electronic items to computers discarded by their users [1] . Electronic waste contains valuable metals as well as lead, mercury, nickel, selenium, cadmium, polybrominated diphenyl ethers, and polychlorinated biphenyls which are potentially environmental contaminants. E-waste is commonly disposed in landfills. Although illegal under the Basel Convention, developed and wealthy countries export large quantities of electronic waste to less developed countries, where the processes of recycling include burning and dissolution in strong acids with less consideration to protect human health and the environment. Such reprocessing initially leads to extreme localized pollution followed by migration of the pollutants into receiving aquatic environments (usually as non-point sources) and food chains [1] [2] .

In aquatic environments, larger organisms such as fish have been exposed to heavy metals as a direct consequence of biomagnifications [3] . The danger is that heavy metals even at low concentrations in fish and water have a particular significance in ecotoxicology and their effects have been well documented [4] - [8] . [9] reported a concentration of 0.13 mg/kg manganese and 0.62 mg/kg cadmium in fish. There are recommended limits of individual elements in water and fish [10] . Fishes are the aquatic inhabitants that cannot escape from the toxic effects of heavy metal pollution as a result of their contact with water that carries the heavy metals in solution [8] . The importance of fish in the diet of man cannot be over emphasized and therefore, there is a need to monitor the water quality for fish culturing and the water from which fish is harvested in the natural environment alongside routine screening of fish for heavy metal concentration to limit transfer of heavy metals to man through fish consumption. Water bodies are polluted by run offs, industrial waste discharge and solid waste. This is common in cities closed to water bodies such as lakes, rivers, sea. E-waste (an example of solid waste) disposal can lead to increase in heavy metals concentrations in the environment and in the tissues of living organisms interacting with the polluted environment. When a river in China received discharged waste water from a nearby e-waste processing plant, the organisms in the river had increased heavy metals concentrations in their tissues [11] . Such pollution put living organisms at risk of heavy metal toxicity and human inhabitants relying on such water are also at risk. Lagos State is one of the coastal states in Nigeria, where Alaba International Market is located. This market is known for sales of electronic products both new and fairly used ones. It also has a dumpsite where tons of e-waste are dumped annually. This e-waste dumpsite is close to Lagos lagoon. Run offs from this e-waste dumpsite can easily reach the lagoon, thereby increasing the concentrations of heavy metals released to the lagoon water. This will expose both the micro and macro organisms (including man) to heavy metal toxicity. Hence, the results in this research are geared towards raising public awareness on the danger of improper disposal of e-waste and to provide baseline data on e-waste pollution of aquatic environment.

A total of eleven different fungi species were isolated from the e-waste soil sample, soil without e-waste sample and polluted fish vials, nine of which (Aspergillus niger, Aspergillus flavus, Articulospora inflata, Zoopagenitospora, Varicosporiumelodeae, Penicillium sp., Rhodoturula sp., Rhizopus stolonifer, and Mucormucedo) had also been isolated from crude oil polluted environment, other polluted areas, gastrointestinal tract and agricultural soil. Their presence in the soil samples and the vials could have been as a result of their ability to adapt to different environmental conditions and using wide ranges of substances as nutrient and energy sources [21] - [24] . Fungal colony count from each polluted vial showed that the quantity of fungi was inversely proportional to the quantity of e-waste soil pollution and directly proportional to the quantity of soil without e-waste pollution (Figure 1), indicating possible suppressing effect of the pollution on fungal growth in these vials [25] . E-waste soil and e-waste soil polluted fish vials had significant number of fungal isolates. This could be attributed to high percentage of organic contents and moisture content of the e-waste soil sample (Table 1), which might have encouraged the growth of these fungi [25] .

A total of 956 fungi isolates were obtained from tilapia aquaria by the end of the five-week observation period (Tables 2-9). The occurrence of the fungi species revealed that the untreated vial has the highest number of fungi isolates (Table 2 and Table 9), consistent with a possible suppressing effect of soil pollutants. Aspergillus niger, Aspergillus flavus, Aspergillus repens, Articulospora inflata, Zoopagenitospora, Candida sp., Penicillium italicum, Rhizopus stolonifer, Mucormucedo, Varicosporiumelodeae and Rhodoturula sp. were isolated from vials with soils, regardless of electronic pollution. These microorganisms might have adapted to the presence of e-waste in this environment [26] and probably they can be manipulated in the biosorption of pollutants (especially the heavy metals) from e-waste. This agreed with the findings of [27] , in the bio accumulating of heavy metals using Aspergillus lentulus, [28] , using bacterial and protozoan species and [29] using yeast (Rhodotorula mucilaginosa).

Bioaccumulation of heavy metals occurred in tilapia (Oreochromis niloticus), this could be through oral consumption, the gills or the skin [30] . The sequence of the heavy metals concentrations in Oreochromis niloticus tissue samples was Zn > Mn > Pb > Cr > Ni > Cd > Co (Figure 2). The similarity in the order of magnitude in the heavy metal accumulated by the fishes from the polluted vials (especially the accumulation of zinc) is probably due to the same period spent in the different polluted vials and they are same species of fish with the same metabolic system and the same membrane function. The accumulations could also have been due to inability of the fishes to metabolize the heavy metals or poor metabolism of the heavy metals by the fish. The research also showed that cadmium and nickel were poorly accumulated while cobalt was not accumulated. Probably there is no pathway for their absorption by the fish or the presence of enzymes that could detoxify or metabolized the heavy metals could also lead to the results [31] . The maximum tolerable level for manganese was exceeded in tilapia tissue of one vial with e-waste (Mn accumulates from 0.29 mg/kg in Control to 3.13 mg/kg in TR3; Recommended limit is 0.01 - 0.05 mg/kg for manganese [32] . Therefore there is a potential risk (at least possible bioaccumulation and toxicity of manganese) to inhabitants that depend on river or water body polluted by e-waste.

(Source: [20] ).

This variation in pH could have been as a result of succession of the microorganisms in vials and their different fermentative activities [33] . The pH in the vials shifted from slightly acidic (6.60 - 7.05) in week 1 to neutrality (6.85 - 7.60) in weeks 2 - 5 (Figure 3). Vials polluted with soil without e-waste had higher pH values compared to vials polluted with e-waste soil.

The biochemical oxygen demand (BOD) in vials showed no noticeable differences between the soil types (e-waste soil and soil without e-waste) pollution, with week 2 - 5 having higher BOD than the first week (Figure 4). These could be due to similarity in the rate of release of metabolites by tilapia in the vials.

It was apparent from the present study that fungi population and fungi community were influenced by the e- waste presence. Fungi community and activities might eventually be affected by the e-waste presence, if e-waste

persisted in their habitat. Tilapia fish is possibly at a great risk of manganese toxicity since this was present be- yond the recommended tolerable standard. Consumption of heavy metal-contaminated fish by human can lead to heavy metal toxicity in man. These metals can cause gastric and esophageal ulceration in humans and animals. The Agency for Toxic Substances and Disease Registry suggests that ingesting high levels of zinc for several months may cause anemia, damage to the pancreas, and decreased levels of high density lipoprotein. High levels of manganese can cause lung, liver, and vascular disturbances, declines in blood pressure, reproductive abnormalities, and brain damage. Since electrical/electronic equipment and gadgets are also necessary, there should be

guidelines laid down for the proper disposal of e-waste, if they are not recycled.

The author is grateful to the Department of Microbiology and the Department of Fish and Aquaculture Technology, Federal University of Technology, Akure, Ondo State, Nigeria for providing a conducive research environment and items used for this study.

Adeyemi Isaac Sanusi, (2016) Heavy Metal Profile of <i>Oreochromis niloticus</i> Harvested from E-Waste Polluted Vials and Associated Fungi. Advances in Microbiology,06,555-565. doi: 10.4236/aim.2016.68056