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OIL SPILLAGE
IN NIGERIA'S NIGER DELTA
PSYCHO-MORPHOLOGICAL & EMPIRICAL OVERVIEW
PRIMARY AUTHORS/RESEARCHERS:
CHIEF M. L. EFERE
DR. PROSPER AYAWEI
8.1 Bio-Physico-Chemical Parameters
1. Dissolved Oxygen
2. Carbon Dioxide level
3. pH
4. Turbidity
5. Hydro Carbon (petroleum) content of soil
8. 2 Water Test [Surface]
The crude oil samples obtained from the spill source was determined
and has the following key approximate physical properties (obtained at
water surface and therefore could vary).
a. Viscosity = 97.05kg/m.h
b. Density tension = 830.00kg/m³
c. Surface tension = 0.0320n/m
d. Cohesion force = 0.0600n/m
e. Adhesive force = 0.6500n/m
f. Viscosity of oil/water ratio = 2.445
These results show the fast spreading rate of the crude oil once
discharged into the aquatic environment.
8.3 WATER TEST [Fish Ponds]
Water samples were collected from fishponds within the area under
review to Analyse the desired parameter. Tests were carried out at intervals
of 2 weeks.
8.3. 1. Period of inspection.
A | = | 1st test results 29th January - 12th February 1998 |
B | = | 2nd test results 13th February - 27th February 1998 |
C | = | 3rd test results 28th February - 13th March 1998 |
8.3.2. pH: The pH values for the last test results were on the basis of average per sample.
Mean = 4.0 + 3.7 + 3.5 + 3.8 + 4.2 + 4.4 = 3.9
The relationship between pH to pond fish culture is summarized
below.
Death Slow growth Good growth Slow growth Death
4 | 5 6 | 7 8 | 9 10 | 11 |
Fig: Effect of pH on pond fish (swingle, 1969).
In comparison, the value of 3.9 obtained from the result shows
a slight decrease from acceptable fish survival limit.
8.3.3 ALKALINITY
The term alkalinity refers to the total concentration of bases in water expressed in milligram per litre equivalent to the carbonate.
Alkalinity measurement ranged between 95 - 130, thus depicting a fluctuating yield.
Total Alkalinity (mg/l) No. ponds Average Yield kg/ha
8 - 20 | 7 | 19 |
21 - 40 | 7 | 32 |
41 - 80 | 20 | 71 |
81 - 120 | 15 | 70 |
>120 | 20 | 54 |
Fig: Annual yield of yellow pikeperch (stizostedron vitereum) in
ponds with waters of different total alkalinities (Moyle, 1946).
8.3.4 DISSOLVED OXYGEN
The BOD level in the waters analysed show decrease in the universally
accepted level for fish survival.
A | 0.8 | 0.9 | 0.7 | 1.2 | 0.9 | 0.9 |
B | 1.2 | 1.0 | 0.7 | 0.9 | 0.7 | 0.8 |
C | 0.9 | 0.9 | 1.0 | 0.8 | 1.0 | 0.9 |
,
A | = | 5.4 | B | = | 5.3 | C | = | 5.5 |
T | = | A + B + C | = | 5.4+ 5.3 + 5.5 | ||
= | 16.2 | |||||
C | = | (16.2)²
3 X 6 |
= | 262.4
18 |
= | 14.57 |
= | 14.6 |
yij² = (0.8)² + (0.9)² + (0.7)²
+(1.2)² +(0.9)²+ (0.9)²+(1.2)²
+ (1.0)² + (0.7)² + (0.9)² + (0.7)²
+
0.8)² + (0.9)² + (0.9)²
+ (1.0)² + (0.8)² + (1.0)² + (0.9)²
= 0.64 + 0.81 + 0.49 + 1.44 + 0.81+
1.44 + 1 + 0.49+ 0.81 + 0.49 +0.64 + 0.81+ 0.81 + 1 +
0.64 + 1 + 0.84
= 14.97
SST = 14.97 - 14.6 = 0.37
T1²
n |
= | (5.4)²
+ (5.2)² + (5.5)²
6 |
= | 87.5
6 |
= | 14.58 |
SS(Tr) | = | 14.58 - 14.57 | = | 0.01 |
SSE | = | 0.37 - 0.01 | = | 0.36 |
K - 1 | = | 3 - 1 | = | 2 |
K(n-1) | = | 3(6 - 1) | = | 15 |
NK - 1 | = | 18 - 1 | = | 17 |
Ms(Tr) | = | 0.01
2 |
= | 5 x 10-3 |
MSE | = | 0.36
15 |
= | 2.4 x 102 |
F | = | 5 x 10-3
2.4 x 10-2 |
= | 0.2 |
Calculated F value is far less than tabulated values at 99%, 95%, 90%,
85%, 80%, 70%, 75% confidence level. Therefore, the authenticity of the
sampling method is very high.
8.3.5 Anova: Determining water sampling method relative to fish survival
(oxygen count, BOD).
Source of Error | Df | SS | Ms | F |
Samples | 2 | 0.01 | 5 x 10-3 | 0.2 |
Error | 15 | 0.36 | 2.4 x 10-2 | |
Total | 17 | 0.37 |
NOTE: This results in a slight decrease in the universally accepted value of 1mg/litre for fish survival. Thus some specie of fish will definitely die of the spill.
8.3.6 CARBON DIOXIDE LEVEL:
Measurement here are in parts per million (PPm)
A | 60 | 50 | 72 | 100 | 78 | 50 |
B | 65 | 84 | 75 | 105 | 80 | 69 |
C | 80 | 90 | 80 | 105 | 85 | 77 |
A | = | 410 | B | = | 478 | C | = | 517 |
T | = | 410 + 478 + 517 | = | 1405 |
C | = | (1405)²
18 |
= | 109668.06 |
Y²ij = (60)2
+(50)² +(72)² + (100)² + (78)²
+ (50)²+ (65)² + (84)² + (75)²
+ (105)² +
(80)² + (90)² + (80)² + (105)²
+ (85)² + (77)²
= 3600 + 2500 + 5184 + 10000 + 6084 + 2500 + 4225 + 7056 + 11025 + 6400
+ 4761 +
6400 +8100 + 6400 + 11025 + 7225 + 5929
= 114039
SST = 114039 - 109668.06 = 4370.94
T²
= (410)² + (478)² + (517)²
= 110645.5
n
6
SS(Tr) = 110645.5 - 109668.06 = 977.44
SSE = 4370.94 - 977.44 = 3393.5
K - 1 = 2, Kn - 1 = 15, nK - 1 = 17
Ms(Tr) = 977.44
= 488.72
2
MSE = 3393.5
= 226.23
15
F
= 488.72
= 2.16
226.23
Calculated value highly feasible at even 50% confidence levels.
8.3.7. Anova: Determining carbon dioxide count relative to fish survival
Source of Error | Df | SS | Ms | F |
Samples | 2 | 977.44 | 488.72 | 2.16 |
Error | 15 | 3393.5 | 226.23 | |
Total | 7 | 4370.94 |
8.4 SOIL TEST (RIVER BANKS)
Gravimetric analysis was used to determine amount of petroleum
in a given sample using Benzene as solvent. Soil samples were collected
at the sites using the riverbanks as the focal points.
Samples | Top Soil (mg/m) | 25cm depth Soil (mg/m) |
A | 70 | 75 |
B | 50 | 60 |
C | 101 | - |
D | 89 | 94 |
E | 76 | 85 |
F | 63 | 70 |
To determine whether there exist some significance in the amount of petroleum at various sites, the F-test was determined.
Let top soil be X0
Let 25cm depth soil be X1
Xo | = | 449 | X1 | = | 384 | |
Xo | = | 449
6 |
X1 | = | 384
5 |
|
= | 74.8 | = | 77 | |||
(X - Xo)² | = | 1267 | (X - X1)² | = | 695 | |
F(Vo,V1) | = | So2
S12 |
||||
So² | = | (Xo - X1)²
n |
= | 1267
6-1 |
= | 253.4 |
S1² | = | (X0 - X1)² | = | 695
5-1 |
= | 173.75 |
The tabulated F value for Vo = 5 and V1 = 4 is 6.25
F expt = 253.4
= 1046
173.75
F expt < F crit
This value of F was tested at various confidence levels to be extremely
accurate.
8.5. pH
The pH values for the above tests were determined on the basis of average
per sample.
8.6. Turbidity:
The turbidity of the waters analysed show a very sharp rate. Since fish
survive better in clean water, it could be deduced that fish survival in
the affected area is impossible.