Research Article (Open access) |
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Int. J. Life. Sci. Scienti. Res.,
4(4):
1940-1945,
July 2018
Microbial,
Hydrobiological Indicators and Physicochemical
Characteristics of a Remote Aviation Fuel-Contaminated Lentic
System in Ibeno, Nigeria
Justina Ime R. Udotong1*, Ime
R. Udotong2, Unyime P. Udoudo3
1Senior
Lecturer, Department of Biochemistry, Faculty of Basic Medical Sciences,
University of Uyo, Uyo, Akwa Ibom State, Nigeria
2 Professor, Department of Microbiology, Faculty of
Science, University of Uyo, Uyo,
Akwa Ibom State, Nigeria
3Postgraduate Student, Department of Fisheries and
Aquatic Environmental Management, Faculty of Agriculture, University of Uyo, Uyo, Akwa
Ibom State, Nigeria
*Address
of Corresponding Author: Dr
Justina Ime R. Udotong, Senior Lecturer, Department of Biochemistry, Faculty of Basic Medical Sciences,
University of Uyo, Uyo, Akwa Ibom State, Nigeria
ABSTRACT- This research paper presents the microbial and hydrobiological indicators and the physicochemical quality
of water samples from a lentic ecosystem in Ibeno LGA, Nigeria, after sixteen (16) years of an aviation
fuel spill. Using culture-dependent methodologies, the hydrocarbonoclastic
bacterial and fungal counts (HBC & HFC) ranged from 3.4 x 104 to
1.2 x 105cfu/l and 4.7 x 103 to 1.8 x 104 cfu/l, respectively with the ratios of total heterotrophic
bacterial counts to HBC and total fungal counts to HFC ranging from 8 to 12%
and 15 to 22%, respectively. Predominant bacterial indicators included Pseudomonas aeruginosa, Bacillus subtilis,
Micrococcus varians and Enterobacter aerogenes
while predominant fungal indicators included Aspergillus niger, A. terreus,
Candida sp, Saccharomyces
sp, Phoma
sp. and Botrytis sp. Predominant
zooplanktons in the sampled area were rotatoria while
the least were nematodes and followed the trend: Rotatoria
> Copepoda > Cladocera
> Nematoda. Water samples from the area showed
evidence of oil sheen when disturbed; with pH values (6.2 to 7.8) tending
generally towards neutral. Total petroleum hydrocarbon (TPH) from this aviation
fuel-contaminated lentic system ranged from 81.5 mg/l
to 505.2 mg/l. Dissolved oxygen (DO) were generally low with high BOD and COD
of 46.3 mg/l and 321.1mg/l, respectively. Other physicochemical parameters were
typical of lentic ecosystems in the Niger Delta
region,
Keywords: Aquatic pollution, Aviation fuel, Hydrobiological parameters, Hydrocarbonoclastic
Microorganisms, Lentic ecosystem, Physicochemical
characteristics
INTRODUCTION- Oil
spills occur in the Niger Delta environment almost on a daily basis as a result
of a number of causes including well blow-out, pipeline rupture, sabotage,
equipment failure, etc. According to Udotong [1],
Leonardi et al.
[2], and Udotong
et al. [3] there are
therefore a number of oil-contaminated sites in the region. On 8th
August 2001, the 30-year-old 4” QIT-Jetty Aviation fuel pipeline ruptured
resulting in the spillage of about 1,000 barrels of Aviation fuel into the
environment of Inua Eyet Ikot in Ibeno local government
area of Akwa Ibom State,
Nigeria. The aviation fuel spillage continued at high pressure for more than 3
hours before it was stopped. The spilled aviation fuel drained into Akpauchat swamp, a lentic
ecosystem in Ibeno in the Niger Delta region of
Water samples from this contaminated lentic system in Ibeno in the
Niger Delta region of Nigeria were characterized using standard methods,
sixteen years after aviation fuel spill; with a view to documenting predominant
microbial and hydrobiological indicators and
physicochemical characteristics of such remote Aviation fuel-contaminated
site.
MATERIALS AND METHODS
Description of
Study Area and Sample Collection- The
aviation fuel-contaminated site is located at No 65A Qua Iboe Terminal (QIT) road at Inua Eyet Ikot village in Ibeno LGA of Akwa Ibom State, Nigeria (Fig. 1). The spill site lies within Longitude 7o30’ to
8o00’E and Latitude 4o30’ to 4045’N
on the South Eastern Nigerian Coastline. The study site (Fig. 2) is a swamp and thus a lentic system. Field sampling for this study was embarked
upon from 25th April 2016 to 2nd August 2016. Water
samples were collected at three (3) locations from this aviation
fuel-contaminated site using sterile plastic containers for microbiological, hydrobiological and physicochemical analyses. The samples
for microbiological analyses were stored in ice-packed coolers and were
transported to the Microbiology Laboratory for analyses. These and other
samples for physicochemical and hydrobiological
analyses were transported to the Fisheries and Hydrobiology Laboratory of
University of Uyo, Uyo,
Nigeria for analyses.
Fig. 1: Map of Akwa Ibom State
showing Sampling location at Ibeno
Microbiological
Analysis
Ten-fold serial
dilution of Samples, Inoculation, and Incubation- Serial ten-fold dilutions of each of the samples
were prepared according to the methods of Collins and Lyne
[4] and Harrigan and McCance
[5]. Appropriate dilutions were inoculated onto appropriate nutrient
media and were incubated. Hydrocarbonoclastic
microorganisms were determined using the mineral salt medium (MSM) as described
by Okpokwasili and Okorie [6].
After incubation, discrete microbial colonies were counted and multiplied by
the reciprocal of the dilution factor and expressed in colony forming units per
millilitre (cfu/l) and
their respective cultural morphologies were observed and recorded.
Purification and
Maintenance of Pure Culture of Isolates- Discrete
colonies were purified by repeated sub-culture onto appropriate nutrient media.
Pure cultures were preserved on nutrient agar slants and stored in the
refrigerator for further characterization and identification.
Fig. 2: The aviation
fuel-contaminated site
Characterization
and Identification of Microbial Isolates- Pure
cultures of microbial isolates were identified based on cultural parameters,
microscopic techniques and biochemical tests including carbohydrate utilization
Cruickshank et al. [7].
Identification of the bacterial isolates was accomplished by comparing the
characteristics of the cultures with that of known taxa
as in Holt et al. [8].
Characterization and identification of fungal isolates were
carried out as in Domsch et al. [9] and Hunter [10].
Analyses for Hydrobiological
Indicators- Characterization of the
limnological indicators of this system was carried
out. The periphyton removed from substrata were fixed
and preserved in 0.5% acetic lugol, except for
samples for determination of diatoms, which were preserved in 4% formalin.
Techniques of oxidization and preparation of permanent slides of diatoms
followed the method of Simonsen [11].
After this taxonomic analysis, organisms were quantified using an inverted
microscope at 400X, according to methods of Utermöhl [12].
Additional counts were made on permanent slides (100 individuals) to
differentiate very similar diatom species as recommended by Biggs [13].
The
classification system used was that of Round [14]. The systematic
arrangement and generic diagnoses followed Bourrelly [15],
except for the classes Cyanophyceae and Bacillariophyceae, which were classified according to Gleitler [16] and Krammer
& Lange-Bertalot [17], respectively.
Counting of phytoplankton was done by the direct census method of Jhingran et al. [18]. The rates of
primary production of the surface water were estimated as per the standard
"Light and dark bottle method" (Gaarder
& Gran) [19].
Physicochemical
Analysis of water samples- Water quality
parameters viz., temperature, suspended particulate matter (SPM),
transparency, salinity, pH, carbon dioxide, alkalinity, dissolved oxygen (DO),
chemical oxygen demand (COD) and nutrients (nitrate, ammonia, phosphate and
silicate) were determined following standard methods (APHA; FWPCA; Philbert; Strickland and Parson [20-23].
Extinction coefficient (Kt) was estimated from the formula, Kt = 1.44/Secchi depth in meter Holmes 24]. For the
collection of phytoplankton, five liters of water were collected in a plastic
bottle and fixed with Lugol's iodine.
Results Microbiological Indicators-
The
results of total heterotrophic bacterial and fungal counts (THBC & TFC)
ranged from 3.4 x 104 to 1.2 x 105 cfu/l
and 4.7 x 103 to 1.3 x 104 cfu/l,
respectively with the ratios of hydrocarbonoclastic
bacterial counts to THBC (HBC /THBC) and Hydrocarbonoclastic
fungal counts to total fungal counts (HFC/TFC) ranging from 8% to 12% and 15%
to 22%, respectively (Table 1).
Table
1: Microbial Counts of Remote Aviation fuel-contaminated lentic
system
Sample
Code |
THBC
(cfu/ml) |
HBC
(cfu/ml) |
HBC/THBC |
TFC
(cfu/ml) |
HFC
(cfu/ml) |
HFC/TFC |
AFW
– 1 |
5.8 x 104 |
5.8 x 103 |
10% |
6.4 x 103 |
1.2 x 103 |
19% |
AFW
– 2 |
1.2
x 105 |
1.4 x 104 |
12% |
1.3
x 104 |
2.9 x 103 |
22% |
AFW
– 3 |
3.4
x 104 |
2.7 x 103 |
8% |
4.7
x 103 |
7.1 x 102 |
15% |
Legend: THBC- Total Heterotrophic Bacterial count; HBC- Hydrocarbonoclastic
Bacterial Count; TFC- Total Fungal Count; HFC- Hydrocarbonoclastic
Fungal Count
Predominant Microbial Isolates- Predominant
bacterial indicators isolated from this remote aviation fuel-contaminated lentic system were Pseudomonas aeruginosa, Bacillus subtilis, Micrococcus varians,
Enterobacter aerogenes
and Aeromonas sp while predominant fungal indicators
isolated were Aspergillus niger, A. terreus, Candida sp, Saccharomyces sp, Phoma sp and
Botrytis sp.
Hydrobiological Indicators- Diatoms
were the most abundant phytoplankton group in this aviation fuel-contaminated lentic system followed by the dinoflagellates
and Blue green algae. In terms of species richness, the periphyton
groups identified at this site followed the sequence Bacillariophyceae>
Cyanophyceae> Chlorophyceae>
Euglenophyceae. Predominant zooplanktons in this
aviation fuel-contaminated lentic system were in the
sequence of Rotatoria > Copepoda
> Cladocera > Nematoda.
Physicochemical
Characteristics of water samples- Most
of the water samples from the study area were colorless and clear but with
evidence of oil sheen when disturbed; with pH values (6.2 to 7.8) tending
generally towards neutral. Total petroleum hydrocarbon (TPH) in water samples
from this aviation fuel-contaminated lentic system
ranged from 81.5 mg/l to 505.2 mg/l. Dissolved oxygen (DO) was low with high
BOD and COD of 46.3 mg/l and 321.1mg/l, respectively (Table 2).
Table
2: Physicochemical Characteristics of water samples
Parameters |
Sample Code |
||
AFW – 1 |
AFW – 2 |
AFW – 3 |
|
Colour |
Colourless / Clear |
Colourless / Colour |
Colourless / Colour |
pH |
7.8 |
6.2 |
7.0 |
TPH (mg/l) |
276.1mg/l |
505.2mg/l |
81.5mg/l |
DO (mg/l) |
7.0 |
12.0 |
8.0 |
BOD (mg/l) |
43.0 |
46.3 |
44.2 |
COD (mg/l) |
302.0 |
321.1 |
311.1 |
Heavy metals Fe (mg/l) Pb (mg/l) Cu (mg/l) Cd (mg/l) Zn (mg/l) Mg (mg/l) Mn (mg/l) Co (mg/l) |
10.5 |
8.3 |
12.0 |
0.02 |
0.01 |
0.03 |
|
0.01 |
0.02 |
0.01 |
|
0.01 |
0.01 |
ND |
|
0.1 |
0.1 |
0.1 |
|
0.01 |
0.01 |
0.01 |
|
0.01 |
0.01 |
ND |
|
0.01 |
ND |
0.01 |
ND– Not Detected
DISCUSSION- These
ratios of hydrocarbonoclastic bacteria count to THBC
in excess of 1% are indicative of petroleum hydrocarbon input into this lentic system. All the microbial isolates listed are
known crude oil-degrading microorganisms Ijah [25];
Udotong [1]; Udotong
et al.[26]. The
dominance of diatoms in this contaminated site may be due to the fact that food
storage in diatoms takes the form of oil droplets and it is thought that
petroleum deposits may represent the pre-historic accumulation of an incredible
number of such droplets from Diatoms and other groups of plankton. Specific phyto- & zoo-plankton indicators at this aviation
fuel-contaminated lentic system are listed in Akpan and Akpan [27].
The observed dominance of these indicators in terms of species richness has
been a common feature at hydrocarbon-contaminated lentic
systems and is typical of a biologically productive freshwater ecosystem in the
Niger Delta region, Nigeria Akpan and Akpan [27]. About 80% of all water
samples from this study area had some heavy metals (Fe, Pb
and Cu) concentrations in excess of WHO maximum permissible levels for drinking
water. All other physicochemical parameters of this aviation fuel-contaminated lentic system were typical of lentic
ecosystems in the Niger Delta region, Nigeria (RPI) [28].
CONCLUSION- About sixteen years after the spill, the lentic system was seen to be contaminated. Although natural
processes are ongoing at this aviation fuel-contaminated lentic
system in the past sixteen years, there is need for enhanced decontamination
(bioremediation) of this and many other such sites that exist in the Niger
Delta region in Nigeria. Integrated bioremediation including phytoremediation techniques has been advocated.There
are on-going researches by these authors to monitor microbial (eubacteria, archaea and eukarya) diversity at this site using metagenomics
and other omics approaches with a view to identifying
efficient hydrocarbonoclastic microorganisms that can
be used for effective bioremediations of this and other such polluted sites in
the Niger Delta Region. This
research is one of the pioneering efforts at bioremediation of petroleum
hydrocarbon polluted sites in Nigeria.
CONTRIBUTION
OF AUTHORS
Justina Ime Rufus Udotong- Literature search, Sample collection and samples/
data analysis and interpretation and writing of article for Physicochemical
Characteristics, critical review and final approval
Ime Rufus Udotong-
Literature search, Sample collection and samples/ data analysis and
interpretation, writing of article for Microbial characteristics and article
review.
Unyime Patrick Udoudo- Literature
search, Sample collection and samples/ data analysis and interpretation,
writing of article for Hydrobiological
characteristics.
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Harrigan WF, McCance ME.
Laboratory methods in food and diary microbiology. London; Academic Press:
1990.
6.
Okpokwasili GC, Okorie BB. Biodeteroriation potentials of microorganisms isolated from
Car Engine Lubricating oil Tribology International,
1988; 21: 215-220.