the aquatic macrophytes and physico-chemical …article.aascit.org/file/pdf/9760734.pdfvalue as the...
TRANSCRIPT
AASCIT Journal of Environment
2015; 1(3): 41-47
Published online July 20, 2015 (http://www.aascit.org/journal/environment)
Keywords Diversity,
Abundance,
Aquatic Macrophytes,
Physcio-Chemical Parameters,
Ebonyi River
Received: June 30, 2015
Revised: July 6, 2015
Accepted: July 7, 2015
The Aquatic Macrophytes and Physico-Chemical Parameters of Ebonyi River Southeastern Nigeria
Uneke Bilikis Iyabo, Okereke Amarachukwu
Dept. of Applied Biology, Faculty of Biological Sciences, Ebonyi State University, Abakaliki,
Ebonyi State, Nigeria
Email address [email protected] (U. B. Iyabo), [email protected] (U. B. Iyabo)
Citation Uneke Bilikis Iyabo, Okereke Amarachukwu. The Aquatic Macrophytes and Physico-Chemical
Parameters of Ebonyi River Southeastern Nigeria. AASCIT Journal of Environment.
Vol. 1, No. 3, 2015, pp.41-47.
Abstract Aquatic plants contribute to maintaining key functions with its economic importance and
related biodiversity in freshwater ecosystems, and to provide the needs of human societies.
The way the ecological niches of aquatic macrophytes are determined by
physico-chemical parameters which include the dissolved oxygen (mg/dl), water t(°C),
total dissolved solids(mg/dl), flow rate of the river (m/s), conductivity (µs/cm) and the pH
value as the abiotic factors were considered. A simple, broadly applicable model of the
distribution of growth forms according to these physico-chemical parameters was
discovered. The aquatic macrophytes diversity and abundance in Ebonyi River was as
follows with the family of Cyperaceae and Poaceae having the greatest abundance
followed by Onagraceae, while Amaranthaceae, Araceae, Asteraceae, Hydrophyllaceae,
Leguminosae, Polygonaceae and Pontederiaceae were least abundant. The above
mentioned physcio-chemical parameters also varied within period of study their mean
deviations as follows; dissolved oxygen (5mg/l), water temperature (29.17 °C), pH (7.70),
total dissolved solids (18.0mg/dl), conductivity (38.33µs/cm) and flow rate (7.97 m/s).
The pH was discovered to be indirectly proportional to the number of aquatic macrophytes;
lesser pH leading to greater aquatic macrophytes while greater number of aquatic
macrophytes leads to lesser total dissolved solids.
1. Introduction
Aquatic plants are of two types, which are the aquatic microphytes and aquatic
macrophytes. Aquatic microphytes are those that are microscopic in nature and cannot be
easily seen with the naked eyes, example includes; the phytoplanktons, diatoms, etc.
Aquatic plants (macrophytes) are plants that have adapted to living in aquatic
environments (saltwater or freshwater). They are also referred to as hydrophytes or
macrophytes. These plants require special adaptations for living submerged, in or at the
water's surface. The most common adaptation is aerenchyma, but floating leaves and
finely dissected leaves are also common (Agbogidi et al., 2000). Aquatic plants can only
grow in water or in soil that is permanently saturated with water. They are therefore a
common component of wetlands and rivers (Keddy, 2010). The principal factor
controlling the distribution of aquatic plants is the depth and duration of flooding.
However, other factors may also control their distribution, abundance, and growth form,
including nutrients, disturbance from waves, grazing, and salinity. Aquatic vascular plants
have originated on multiple occasions in different plant families; they can be ferns or
angiosperms (including both monocots and dicots). Seaweeds are not vascular plants;
rather they are multicellular marinealgae, and therefore are not typically included among
42 Uneke Bilikis Iyabo and Okereke Amarachukwu: The Aquatic Macrophytes and Physico-Chemical Parameters of
Ebonyi River Southeastern Nigeria
aquatic plants. A few aquatic plants are able to survive in
brackish, saline, and salt water. Examples are found in genera
such as Thalassia and Zostera. Although most aquatic plants
can reproduce by flowering and setting seed, many also have
extensive asexual reproduction by means of rhizomes, turions,
and fragments in general. One of the largest aquatic plants in
the world is the Amazon water lily; one of the smallest is the
minute duckweed. Many small aquatic animals use plants like
duckweed for a home, or for protection from predators (Ezeri
et al., 2003 and Chowdhury et al., 2008). But areas with more
vegetation are likely to have more predators. Some other
familiar examples of aquatic plants might include floating
heart, water lily, lotus and water hyacinth (Keddy, 2010). A
river is a natural flowing watercourse, usually freshwater,
flowing towards an ocean, a lake, a sea, or another river. In
some rare cases a river could flow into the ground and dry up
completely at the end of its course, without reaching another
body of water. At the bank on the river is a wetland which is a
land transitional between terrestrial and aquatic system where
soil is frequently waterlogged and is able to sustain life like
aquatic plant (Bell, 1992; Bornette et al., 2008). Thus this
study is aimed at providing the general knowledge of aquatic
plants, the knowledge of the economic importance of aquatic
macrophytes, the diversity of the aquatic macrophytes present
in Ebonyi River and the physico-chemical characteristics of
the river.
2. Materials and Methods
2.1. Study Area
Ebonyi state is located in the Southeastern Benue trough of
Nigeria. The main study area falls within the climatic region
of Southeastern Nigeria where the rainy season spans from
April to October and the dry season from October to April.
The average annual rainfall of the study area is about 1500mm
with actual surface temperature (seasonal temperature) of
between 24 – 36 °C during dry season and about 18 °C during
rainy season. Ebonyi river is located in Onu-Ebonyi Izzi,
North-Eastern part of Ebonyi State, between latitude of 064`N
and longitude 087`E. The river is a source of water to Izzi
village, utilized for both domestic and agricultural purpose.
The river is about 5km from Abakaliki, the capital of Ebonyi
state (Fig. 1). The river flows throughout the year but flows
heavily during the rainy season.
Fig. 1. Map of Ebonyiriver showing study area.
AASCIT Journal of Environment 2015; 1(3): 41-47 43
2.2. Physico-Chemical Parameters
Water Temperature: Digital thermometer was used to
determine the water temperature in situ each time a trip was
made to the site by dipping thermometer into the water until a
steady value was observed then recorded as the water
temperature in degree Celsius (°C). Flow rate: Flow rate was
determined in situ using cock, stop watch and time. The
distance covered by the flowing cock within a specific period
was recorded and flow rate calculated as d/t
Where d= distance covered in meters (m)
Time= time taken in seconds (s)
Hydrogen Ion Concentration (pH): This was determined in
situ using Hanna pH meter model HI96107. The metre was
calibrated using pH buffer at 8.9 then dipped in the water
sample until steady value was read, then recorded as pH
values.
Dissolved Oxygen (DO): The amount of dissolved oxygen
was determined in situ by winkler’s methods
a. A 300ml glass stopper BOD (Biological Oxygen Demand)
bottle was filled with the water sample ensuring that there
were no air bubbles.
b. 2ml of Manganese (ii) sulphate was added to the
collection by inserting a calibrated pipette just below the
surface of the liquid and the pipette squeezed out slowly
to ensure that bubbles are not introduced into the sample
through the pipette.
c. 2ml of alkaline potassium iodide solution was added into
the sample in the same manner as in b.
d. The bottle was carefully covered with a stop cock
ensuring that air was not introduced and the sample
mixed by inverting the bottle severally. The sample was
checked for air bubbles and if found, the sample was
discarded. The presence of oxygen in the sample was
noticed by the appearance of a brownish-orange cloud of
precipitate.
e. 2ml of concentrated Hydrogen-tetra-oxosulphate (vi)
acid was added to the sample. The bottle was carefully
covered and inverted severally dissolving the precipitate,
thus making the sample to be a ‘fixed’ solution.
f. 2ml of the sample in a glass was titrated with
sodiumthiosulphate until a pale straw colour was
obtained. This was done by slowly dropping the
sodiumthiosulphate solution (A ml) from a calibrated
pipette and swirling the sample.
g. 2ml of freshly prepared starch solution was added to the
sample which gave a dark blue colour.
h. Addition of sodiumthiosulphathe (B ml) continued
slowly until the sample turned clear which marks the end
point of the experiment.
i. The concentration of the Dissolved Oxygen in the sample
was equivalent to the millitres of the sodium hiosulphate
used during the titration as 1ml equal 1mg/l dissolved
oxygen. That is, the concentration of Dissolved Oxygen
= Aml + Bml (knowing that 1ml of sodiumthiosulphate is
equal to 1mg/l of Dissolved Oxygen.
Conductivity: This was determined using Hanna
conductivity metre (model H198801). The meter was inserted
in the water in situ and allowed to attain a steady value and
then recorded in (µS/cm).
Total Dissolved Solids (TDS): This was measured using
Hanna TDS metre (model H198801). The meter was inserted
into the water and allowed to attain a steady value; the value
was recorded at TDS (mg/l) (Anene, 2003).
2.3. Collection and Identification of Aquatic
Macrophytes
Aquatic macrophytes were collected along river bank of
Ebonyi River and on the surface water for the floating
macrophytes once each time the trip to the site were made for
the period of three months; both creeping and standing
macrophytes were collected. The macrophytes collected were
arranged in white paper and covered with brown paper
envelop to avoid drying up. It was quickly transported to
Applied Biology Laboratory for identification. Macrophytes
were identified from family to species level with the use of a
catalogue (Agbogidi et al., 2000).
3. Results
The result of the physico-chemical parameter of Ebonyi
River shown in Table 1 explained the different values
obtained/recorded in the different parameters during the study
period. Dissolved oxygen was highest in the month of
November and lowest in the month of January with a mean of
5 mg/l. The water temperature was recorded highest in the
month of January and lowest in the month of November with
the mean of 29.20C and the pH value was recorded highest in
the month of January and lowest in the month of November,
having a mean of 38.33µS/cm. the flow rate was also recorded
in m/s having its highest speed in the month of December and
lowest speed in the month of January (Fig. 1). The total
dissolved solid (TDS), conductivity, water temperature (WT)
and PH is very high in January, showing that the period is high
in January whereas the Flow rate and the dissolve oxygen (DO)
are very low and the TDS, DO, conductivity and flow rate has
a maximum value in December. The TDS and PH have
minimum value in November (Fig. 1). All through the period
of the study, the family Cyperaceae had the highest number of
species in Ebonyi river seconded by Poaceae and Onagraceae
whereas the Araceae and Hydrophyllaceae had the least
abundance of species (Table 2). Fig. 2 shows the percentage
abundance of each family of the aquatic Macrophytes. This
shows that the families of Poaceae, Cyperceae and
Onagraceae and are favoured in Ebonyi River, whereas the
families of Araceae and Hydrophyllacea are not favoured in
Ebonyi River .
44 Uneke Bilikis Iyabo and Okereke Amarachukwu: The Aquatic Macrophytes and Physico-Chemical Parameters of
Ebonyi River Southeastern Nigeria
Table 1. Mean and Standard Deviation of Physico-chemical parameters of Ebonyi River.
Physico-chemical parameters Max. Min. Mean±Standard deviation
Dissolved oxygen (Mg/L) 5.2 4.8 5.00±0.20
Water temperature (°C) 32.8 26.6 29.17±3.24
pH-value 8.2 7.1 7.70±0.57
Total Dissolved Solids (Mg/L) 21 15 18.00±3.00
Conductivity (µS/Cm) 45 32 38.33±6.51
Flow rate (M/S) 8.3 7.5 7.97±0.42
Table 2. The relative abundance of the species found during the period of study.
FAMILY Species Abundance
AMARANTHACEAE Alteranthera sessilis +
Total 1
ARACEAE Pisia stratiotes +
Total 1
ASTERACEAE Eclipta alba +
Total 1
CYPERACEAE
Cyperus iria
Cyperus haspan
Fimbristylis ferruginea
Fimbristylis littoralis
Fuinea aliaris
Kyllinga balbosa
Kyllinga squamulata
+++
Total 7
HYDROPHYLLACEAE Hydrolea palustris +
Total 1
LEGUMINOSAE Neptonia aleracea +
Total 1
ONAGRACEAE
Ludwigia abyssinica
Ludwigia hyssopifolia
Ludwigi octovalvis
++
Total 3
POACEAE
Acrocera zizaniodes
Echinochloa crus-pavonis
Echinochloa pyramidalis
Elytrophorus spicus
Oryza barthii
Panicum laxum
Panicum subalbidum
+++
Total 7
POLYGONACEAE Polygonium lanigerum +
Total 1
PONTEDERIACEAE Eichhornia natais
Heteranthera callifolia +
Total 2
Key: + = present
++ = abundance
+++ = more abundance
AASCIT Journal of Environment 2015; 1(3): 41-47 45
Fig. 2. The summary of the physic-chemical parameters of the water sample.
Fig. 3. The percentage (%) abundance of aquatic Macrophytes by family in Ebonyiriver.
4. Discussion
The various physico-chemical parameters of Ebonyi River
with Dissolved Oxygen ranging from 5.2 to 4.8, having the
mean value of 5.00 during the study period. Higher percentage
of Dissolved Oxygen was observed in the month of November,
2014 with 34.67% and low in the month of January, 2015 with
32.00%. The water temperature of the river ranged from
32.8°C to 36.6°C with an average of 29.17°C and a standard
deviation of 3.24°C. Lower temperature was observed in the
month of November, 2014. The pH values of the river ranged
from 8.1-7.1 with an average of 7.7; this shows that the river is
slightly alkaline, giving the river its fresh water nature. The
Total dissolved solids ranged from 21-15 (mg/l) with a mean
of 18 and standard deviation of 0.57, having a higher TDS in
the month of January and lower in the month of November.
The conductivity ranged from 45-32 (µS/cm) with a mean of
46 Uneke Bilikis Iyabo and Okereke Amarachukwu: The Aquatic Macrophytes and Physico-Chemical Parameters of
Ebonyi River Southeastern Nigeria
38.33 (µS/cm) and a standard deviation of 6.51. Higher
percentage was observed in the month of January. The flow
rate of the river ranged from 8.3-7.5 with a mean of 7.97 and
standard deviation of 0.42. Higher percentage was observed in
the month of December and lowest in the month of January.
The variation of these parameters may probably be due to the
change in weather condition during the study period (Cooley,
1996). The different species of aquatic macrophytes found
during the study period and its abundance using the number of
species belonging to various families indicates that the species
found are common aquatic macrophytes found around the
wetlands of the South-Eastern part of Nigeria (Ayeniet al.,
1999). A total number of 10 families (Amaranthaceae,
Araceae, Asteraceae, Cyperaceae, Hydrophyllaceae,
Leguminoceae, Onagraceae, Poaceae, Polygonaceae and
Pontederaceae) were identified in the study area with
Cyperaceae and Poaceaehaving highest abundance with +++
and rare abundance was observed in the rest families with +
except Onagraceae which had a sparse abundance of ++. The
percentage abundance of the ten families, highest percentage
abundance was observed with the Cyperaceae family and
lowest was with the Araceae and Hyderophyllaceae. This
statistic shows that the river had more of grass weed
macrophytes than the root knod or leguminous weed
Macrophytes which is in agreement with Ita (1994) who
revealed the abundance of aquatic plants in various parts of
Nigeria. Panicum subalbidumis robust annual or short-lived
perennial with soft herbaceous culms 60-200 cm. high, erect
or decumbent and rooting at the lower nodes, the upper nodes
sharply demarcated. Leaf laminae is 20-50 cm long and 7-15
mm wide, linear, flat, acute or acuminate. Panicle 20-50 cm.
long, ovate or oblong, sparsely to moderately branched, the
tertiary and sometimes the secondary branches appressed at
maturity. Spikelets is (2.7) 3-3.5 mm long, narrowly ovate,
acuminate; inferior glume ¼-1/3 the length of the spikelet,
broadly ovate, 1–3-nerved, obtuse or acute; superior glume
7-9-nerved; inferior lemma similar to the superior glume,
sterile, its palea poorly developed or absent; superior lemma
and palea pallid or dark, glossy (Jackson and Wiehe, 1958).
The plant is found at margins of rivers, lakes and swamps
200-3400 m. It is used as food grain for insects (Jackson and
Wiehe, 1958). Ludwigia hyssopifolia belonging to the family
of Onagraceae also called water primrose, the plant is an erect,
glabrous herb of up to 60cm high that reproduces from seeds.
It is commonly found in lowland rice soil and flood plains of
West Africa. Cyperusiria is a tufted annual sedge up to 75 cm
high that reproduces by seeds and widely spread in many parts
of West Africa belonging to the family of Cyperacea.
Ludwigia abyssinica belonging to the family of Onagraceae,
having a common name of water primrose. It is an erect,
annual or perennial shrub about 1-2m high that reproduces
from seeds. It is commonly found in lowland area. Panicum
subalbidum of the family POACEAE is a tufted swamp grass
up to 2 m high that reproduces from seeds. It occurs in deep
water rice and swamps. It is an erect, tuft, annual grass about
1.5 m high that roots at the nodes and reproduces from the
seeds. The roots are fibrous, well developed, thick and
massive. The stems are rounded and spongy. The leaf blades
are flat, linear, about 40-45 cm long and up to 1.5 cm wide,
rough upper surface and the margins, and taper from the
middle to the fine narrow tip. The inflorescence is dense
panicle about 25 cm long and erect and stiff branches, the
spikelets are flat, oblong, 7-10 mm long, rather deciduous and
with pink awns 4-16 mm long. It is an important weed of
lowland rice, also occurring in swamps and shallow waters
(Ita, 1994). Oryza barthii is a robust, tufted sedge 1-2 m high
that can reproduce from seeds. It has an erect, stout stem
which is triangular in cross-section, thick at the base and
develops numerous fibrous roots. The leaves are large, up to
90 cm long and 2 cm across, taper gradually to the tip and have
broad, overlapping sheaths that clasp the stem below. The
inflorescence is a multi-branched panicle, 25-60 cm long,
subtended by leaf-like bracts which become linear and mjuch
reduced towards the upper part of the plant. The terminal
clusters are larger than the lateral ones and the spikelets are
brown. It is a common weed of swamps often found growing
in rice paddies, irrigation canals and the edges of streams in
the forest zones (Ita, 1994). Rhynchospotra corymbosa (Linn)
Britt.is an erect, branched annual herb up to 60cm high, that
reproduces form seeds. The stem is slightly fleshy but may be
more or less woody at the base. It is often reddish in colour
and root at the nodes. The presence of short stiff hairs makes
the stem feel rough to the touch. The leaves are opposite, ovate
to lanceolate, 2-10cm long and 1-3cm wide pointed at the apex,
rather finely and distantly toothed, and rough on the surfaces.
The upper leaves have no stalks. The inflorescence is made up
of solitary flowers or groups of 2-3 flowers at the tips or in leaf
axils. The flowers are borne on pedicels that are 2-7 cm long.
They are white and hairy with inconspicuous ray florets and
numerous disc florets, each of which is about 1 cm in diameter.
The fruits are pale brown or black achenes, 3 mm long, warty
and wedge-shaped. It can be found in damp and poorly
drained soils, in paddy rice fields, canals and irrigated fields
(Ita, 1994 and Westlake et al., 1998). Eclipta alba is an erect,
glabrous herb of up to 60 cm high, that reproduces from the
seeds. The stem is multi-branched, more or less hollow and is
slightly winged. The leaves are alternate, rather variable in
size, about 2-10 cm long and up to 1.5 cm wide. The flowers
are yellow and in the leaf axils. They are solitary and each has
four sepals and eight stamens. The fruit is a many seeds, linear
capsule that is enlarged at the apical portion where the seeds
are in two rows. The seeds are enclosed in an endocarp. It is a
common weed of lowland rice and flood plains of West Africa
(Sculthrope, 1985 and Sterm, 2000).
5. Conclusion
In conclusion, the physico-chemical parameter study of
Ebonyi River and the identified aquatic macrophytes suggest
that the presence of these macrophytes increases the amount
of Dissolved Oxygen of the river through the exhalation of the
by-product which is oxygen from the photosynthetic process
of the plants. The turbidity of the river which was determined
from measuring the Total Dissolved Solid of the water
AASCIT Journal of Environment 2015; 1(3): 41-47 47
samples is less when the presence of aquatic macrophyteis
high, which indicates that macrophyte has a cleaning effect on
the water. The analysis also suggest that more aquatic
macrophytes are found around the rivers with a slightly
alkaline to neutral pH value river; thus the presence of aquatic
macrophytes in any place depends more on the pH value and
the Total Dissolved Solid of the river.
References
[1] Agbogidi, O.M., Bamidele, J.E., Ekokotu, P.A. and Olele, N.F. (2000). The role and management of aquatic macrophytes in fisheries and aquaculture. Issues on Animal science, 10: 221-235.
[2] Keddy, P. A. (2010). Wetland Ecology and Conservation (2nd Edition). Cambridge University Press. Cambridge, U.K p. 497
[3] Ezeri, G.N.O., Gabriel, U.N. andAshade, O.O. (2003). Effects of partial shading by water lettuce (Pistiastratiotes) on growth of tank cultured Oreochromiiniloticus. Journal of Zoology 2: 29-38.
[4] Chowdhury, M.M.R., Shahjahan, M., Rahman, M.S and Islam, M.S. (2008). Duckweed (Lemna minor) as supplementary feed in monoculture of nile tilapia, Oreochromisniloticus. Journal of Fisheries and Aquaculture Science 3: 54-59.
[5] Bell, P. R. (1992). Green plants. Portland Dioswrides Press, Portland p. 534.
[6] Bornette, G., Tabacchi, E., Hupp, C.R., Puijalon, S. and Rostan, J.C. (2008) A model of plant strategies in fluvial hydrosystems. Journal of Freshwater Biology 53: 1692-1705.
[7] Anene, A. (2003). Techniques in Hydrobiology. In:Eugene, N.O. and O.O. Julian (Eds.), Research Techniques in Biological and Chemical Sciences. Springfield Publishers, pp: 174-189.
[8] Cooley, G. (1996). Global warming. News week, 7(19): 60-68.
[9] Ayeni, J.S.O., Obot, E.A. and Daddy, F. (1999). Aspects of the biology, conservation and management of aquatic vascular plant resources of Nigerian Wetland based on the Kainji lake experience. Proceedings of a Workshop on Sustainable Management and Conservation of Fisheries and Other Aquatic Resources of Lake Chad and the Arid Zone of Nigeria, January 16-17, 1999, Maiduguri, pp: 64-73.
[10] Ita, E.O., (1994). Aquatic plants and wetland wildlife resources of Nigeria. CIFA Occasional Paper No. 21, FAO, Rome.
[11] Jackson, N. W. and Wiehe, C. A. (1958). Anatomy of the check list Nyasal Grass. South African Journal of Aquatic Botany (1): 71-78.
[12] Westlake, D. F., Kvet, J. and Szczepanski A. (1998). The production ecology of wetlands. Cambridge University Press, Cambridge U.K p 568.
[13] Sculthrope, C. D. (1967). The biology of Aquatic Vascular Plant. Königstein-West Germany: Koeltz Scientific Books: p. 597.
[14] Sterm, K. R. (2000). Introductory Plant Biology, Toronto, Ont: McGraw- Hill, p. 433.