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在尼日利亚尼日尔三角洲地区的新卡拉巴尔河上游进行了水和沉积物中重金属的研究。 选择了三个采样站,分别是Choba,Ogbogoro和Aluu。 使用buck科学的原子吸收/发射光谱仪200 A模型收集和分析水和沉积物样品。 水的物理化学参数是原位测量的。 溶解氧的总平均值为4.17±0.83 mg / l,温度的平均值为28.34℃±1.07℃,pH的平均值为5.52±0.54,电导率的平均值为1123.39±859.58μs/ cm,BOD盐度平均值为4.45±1.14 mg / l,盐度平均值为1.47±1.15 ppt,而TDS平均值为598.13±529.58 mg / l。 水中重金属的结果表明,Zn的平均值为1.77±0.53 ppm,Cr的平均值为0.65±0.21 ppm,Pb的平均值为0.19±0.11,Fe的平均值为1.52±0.34 ppm。 沉积物中的重金属表明其浓度高于水中的浓度:Zn的总体平均值为7.90±2.59 ppm,Cr的总体平均值为1.94±0.81 ppm,Pb的总体平均值为2.23±0.61 ppm,而Fe的平均值总平均值为87.43±6.57
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Open Access Library Journal
2018, Volume 5, e4456
ISSN Online: 2333-9721
ISSN Print: 2333-9705
DOI:
10.4236/oalib.1104456 May 8, 2018 1 Open Access Library Journal
Physical and Chemical Parameters and Some
Heavy Metal for Three Rainy Season Months in
Water and Sediments of Upper New Calabar
River, Niger Delta, Nigeria
Awoteinm Dateme Isaiah George
1
, Jasper Freeborn Nestor Abowei
2
1
Department of Fisheries and Aquatic Environment, Faculty of Agriculture, Rivers State University,
Port Harcourt, Nigeria
2
Department of Biological Sciences, Faculty of Science, Niger Delta University, Wilberforce Island, Nigeria
Abstract
The study of heavy metals in water and
sediment was carried out in the upper
reach of the New Calabar River, Niger Delta region in Nigeria. Three sa
m-
pling stations were selected which were Choba, Ogbogoro and Aluu.
Water
and sediment samples were collected and analysed, using the buck scientif
ic
Atomic Absorption/Emission spectrometer 200 A model. Water Phys
i-
co-chemical parameters were measured
in situ
. Dissolved Oxygen had an
overall mean of 4.17 ± 0.83 mg/l, temperature had mean value of 28.34˚C
±
1.07˚C, pH had a mean value of 5.52 ± 0.54,
electrical conductivity had a
mean value of 1123.39 ± 859.58 µs/cm, BOD had mean value of 4.45 ±
1.14
mg/l, salinity had a mean value of 1.47 ± 1.15
ppt while TDS had mean value
of 598.13 ± 529.58 mg/l. Result of heavy metals in water indicated that Zn had
an overall mean value of 1.77 ± 0.53 ppm, Cr had mean value of 0.65 ±
0.21
ppm, Pb had a mean value of 0.19 ±
0.11 while Fe had an overall mean value
of 1.52 ± 0.34
ppm. Heavy metals in sediment indicate higher concentration
than in Water: Zn had an overall mean value of 7.90 ± 2.59
ppm, Cr observed
an overall mean value of 1.94 ± 0.81
ppm, Pb had an overall mean value of
2.23 ± 0.61 ppm, while Fe observed an overall mean value of 87.43 ±
6.57
ppm. The result indicated that the source of heavy metals in the aquatic env
i-
ronment could be industrial effluent, domestic waste, dumping of scrap, vessel
in the water way and runoff from agricultural land.
Subject Areas
Aquaculture, Fisheries & Fish Science
How to cite this paper:
George, A.D.I
. and
Abowei
, J.F.N. (2018) Physical and
Chemical
Parameters and Some Heavy Metal for
Three Rainy Season Months in Water and
Sediments of Upper New Calabar River,
Niger Delta, Nigeria
.
Open
Access Library
Journal
,
5
: e4456.
https:
//doi.org/10.4236/oalib.1104456
Received:
February 28, 2018
Accepted:
May 5, 2018
Published:
May 8, 2018
Copyright © 201
8 by authors and Open
Access Library
Inc.
This work is licensed under the Creative
Commons Attribution International
License (CC BY
4.0).
http://creativecommons.org/licenses/by/4.0/
Open Access
A. D. I. George, J. F. N. Abowei
DOI:
10.4236/oalib.1104456 2 Open Access Library Journal
Keywords
Physico-Chemical Parameters, Heavy Metal, Rainy-Season, Water and
Sediments, Upper New Calabar River
1. Introduction
Heavy metal can be described as a metallic element, which has a relatively high
density as compared to water and is noted for toxicity [1]. Anthropogenic activi-
ties like mining activities, disposal of treated and untreated waste effluents con-
taining heavy metals from different industries e.g. tannery, steel, plants, thermal
power plants and uncontrolled use of heavy metal containing fertilizer and pes-
ticide which enters the aquatic ecosystem through runoff, cause threat to the en-
vironment and bio-organism [2]. Heavy metals are found naturally in the earth
and become concentrated in the aquatic environment as a result of human
caused activities.
Lead is the most prevalent heavy metal contaminant [3]. In water, lead levels
in the aquatic environments of industrialized societies have been estimated to be
two to three times higher than those of pre-industrial level [4]. Heavy metals
pollution of the aquatic environment has long been recognized as a serious en-
vironmental concern. In the sea, pollutants, are potentially accumulated in ma-
rine organisms and sediments, and subsequently transferred to man through the
food chain [5]. For this reason, determination of the chemical quality of waters,
sediments and aquatic organisms, particularly the contents of trace metals is ex-
tremely crucial for human health status [6]. Heavy metal pollutants are of great
concern because they are produced in large amounts and discharged into the en-
vironments. They are toxic to aquatic organisms and bio-concentrate within the
organisms sometimes to the levels greater than that in the environment [7].
Chindah and Nawaguibe [8], reported that heavy metals occur naturally in the
aquatic ecosystem and also as a result of waste discharges from industries and
agricultural runoff, increased urbanization and as a result of increase in human
population. Furthermore, he reported that heavy metals are biologically un-
der-gradable when appeared in higher concentration but easily bio-accumulated
in the tissue of aquatic organisms.
The sediment is a mixture of several components of mineral, species as well as
organic debris, represented as ultimate sink for heavy metal discharge into the
aquatic environment [9]. Yi
et al.
, [10] observed that when heavy metals are dis-
charge into the aquatic environment they can be absorbed by suspended solid
and they strongly accumulate in the sediment. Moreover the sediment acts as a
sink and also as a source of heavy metal [11]. According to Odiete [12] metals
and other fluvial contaminant in suspension or solution do simply flow down
the stream was they form complexes with other compounds, settling in the bot-
tom and absorbed in the sediment.
A. D. I. George, J. F. N. Abowei
DOI:
10.4236/oalib.1104456 3 Open Access Library Journal
Sediments are commonly used as indicators for the degree of pollution in the
aquatic environment [13]. According to Davies
et al.
; [14], heavy metal concen-
trates more in sediment than in water. According to Issa
et al
., [15], sediment is
an integral part of the aquatic environment providing habitat feeding, spanning
and accumulation of heavy metal in the water columns. Contaminated sediment
can cause lethal and sub-lethal effect in benthic and their sediment associated
organism [16]. Sediments are integral part of the aquatic environments provid-
ing habitat, feeding and rearing areas for shell fish, fish and other fauna [12]. It
serves both as a reservoir as well as source of contaminants to the water column.
Usually, the quantity of contaminants found accumulates in sediment to ele-
vated levels.
Water is the most often polluted phase in the environment, which is attri-
buted to the ultimate ending of contaminant in air, soil and land into the aquatic
environment through local precipitation, water surface runoff and leaching of
rock and solid waste [17]. According to Degregori
et al.
, [18], Man’s activities
such as mining, industrial processing of ores and metals, still remain the prin-
cipal cause of the increasing amount of heavy metal in water; which are been
dump in the Aquatic environment. One of the most challenging pollution issues
is the accumulation of heavy metal in water owing to toxicity, abundance, per-
sistence and subsequent bioaccumulation of heavy metal [19]. Omitoyin and
Ajani [20] investigate the accumulation levels of the metals (copper, lead and
zinc) in water samples in addition with studying the feeding habits of fish species
in water, while Ayeloja
et al.,
[21] studied Copper, Lead Cadmium, Zinc, Chro-
mium and Manganese concentration in water. The discharge of heavy metal en-
vironment as pointed out by Abowei and Sikoki [22] that heavy metal could
damage the ecosystem quality rendering water unsuitable to the intending use.
Heavy metal was of critical concern due to their ability to bio-accumulate in
aquatic environment and their toxicity [23] as well as persistency in the natural
environment. Recently different types of biomarkers have been studied and eva-
luated for their acceptability to detect the biological effects as a biomonitoring
tool [24]. According to Dirican
et al
. [25], heavy metals are the most important
forms of aquatic pollutants and may accumulate in the tissues of fish, which are
often at the top of the Aquatic food chain. The progressive and irreversible ac-
cumulation of metal in various organs of aquatic organism always leads to men-
tal related diseases in the long run because of the toxicity of the metals. Among
the aquatic organism, fishes are the important member which often accumulates
metals in different parts of their body. The consequences of heavy metal pollu-
tants in aquatic environment lie in two aspects with respect to their impact.
Firstly, heavy metal has the potency to persist in natural aquatic ecosystems of
an extended period. Secondly they have the ability to accumulate in successive
levels of the biological chain. Thereby causing lethal and sub-lethal diseases [26].
There toxicity has been demonstrated long ago [27]. Exposure to heavy metals
have been linked to developmental retardation [28]. Heavy metal toxicity in-
A. D. I. George, J. F. N. Abowei
DOI:
10.4236/oalib.1104456 4 Open Access Library Journal
clude the binding of heavy metal more strongly to functional site that are nor-
mally occupied by essential functional groups of biologically important mole-
cules, making them inactive, decomposing essential metabolites and changing
the osmotic balance around the cell [29]. The degeneration and malformation of
the cell reflect one aspect of the cytotoxic input after exposure to pollution and
serve as an index of cytotoxicity [30]. Biomonitoring is a promising tool for
identifying pollutants (bio-indicators) that affect human and environmental
health, is especially useful with organisms, which are exposed to biological sys-
tem [31]. According to FAO/WHO [32] water is one of the most valuable natu-
ral resources and it is essential for the maintenance of all forms of life. Water
temperature is one of the most important characteristics of an aquatic ecosys-
tem.
O’connor [33] observed that temperature controls the rate of fundamental bi-
ochemical process in organism and consequently changes in the environmental
temperature which influences population species. Temperature is measured in
Celsius (˚C). Goldman and Horne [34] describe biochemical oxygen demand as
the amount of oxygen required for microbial metabolism of organic compounds
in water. Fish and other aquatic organism may die when oxygen is depleted by
microbial metabolism [35]. Lau
et al.
; [36] describe conductivity as the measure
of the ability to conduct electric current and is the reciprocal of resistance. It was
also observed by Lau
et al.
; [36] that the conductivity ion comes from dissolved
salts and inorganic materials such as alkalis, chlorides, sulfides and carbonate
compound. Conductivity is measured in micro semem per centimeter (µs/cm).
According to WHO [37]. Dissolved oxygen can affect the solubility and avail-
ability of nutrients, which can be released from sediments under conditions of
low dissolved oxygen. Turbidity in open water may be cause by growth of phy-
toplankton and other human activities which can lead to high sediment level en-
tering the aquatic ecosystem. Turbidity is described as the amount of clouding in
water. Turbidity in the aquatic environment is mainly caused by Silt, sand and
mud; Bacteria and other germs; Chemical and precipitates. Turbidity is meas-
ured in Nephelometric turbidity unit NTU [16].
Salinity is a measure of the concentration of the total dissolved salt present in
water. Salinity is measured in part per thousand [38]. Power of Hydrogen (pH)
refers to the measure of hydrogen ions (H
+−
) in water which determine its acidic,
alkaline or neutral character. Any particular water is a mixture of acids and bases
and is the result of acid-base titration processes [39]. Seasonal variation in pH
with higher values in the wet than dry season has been recorded [39]. Situation
of non-seasonality in pH also has been recorded in some tropical rivers by
Chindah and Braide [40] in the New Calabar River; Nkanta [41] in the Bonny
River. Boyd and Lichtkoppler [42] reported that pH of water body rises during
the day and decreases at night due to the removal of carbon (iv) oxide by aquatic
plant between 6.5 and 8; while in natural water pH value ranges from between 4
to 9.
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