)joebxj1vcmjtijoh$psqpsbujpo …downloads.hindawi.com/journals/jmb/2015/376986.pdf · research...
TRANSCRIPT
Research ArticleComposition of Periphyton Community onWater Hyacinth (Eichhornia crassipes) In Analysis ofEnvironmental Characteristics at Ejirin Part of Epe Lagoon inSouthwestern Nigeria
A I Inyang1 K E Sunday2 and D I Nwankwo2
1Department of Marine Biology Akwa Ibom State University Nigeria2Department of Marine Sciences University of Lagos Akoka Nigeria
Correspondence should be addressed to A I Inyang aniefiokinyangyahoocom
Received 7 September 2014 Revised 24 November 2014 Accepted 4 December 2014
Academic Editor Robert A Patzner
Copyright copy 2015 A I Inyang et al This is an open access article distributed under the Creative Commons Attribution Licensewhich permits unrestricted use distribution and reproduction in any medium provided the original work is properly cited
The composition of periphyton community on water hyacinth was investigated at Ejirin part of Epe Lagoon in relation toenvironmental characteristics from December 2012 to May 2013 A total of 14536 individuals of 104 species belonging to fivedivisions were identified with Bacillariophyta (8269) Cyanobacteria (1043) Chlorophyta (563) and Euglenophyta (115)The total species abundance observed showed a strong correlation with rainfall (119903 = 0745) and strongly significant correlationwith TDS (119903 = 0836lowast 119875 gt 005) Biochemical oxygen demand value remained (BOD) le 48mgL while Shannon-Wiener indexvalue remained (119867
119904) le 147 The presence of the following organisms could be used as an indicator of environmentally stressed
aquatic ecosystem euglenoids blue green algae Nitzschia palea Surirella sp Pinnularia sp Gomphonema parvulum Mougeotiasp Spirogyra sp Trachelomonas affinis (Lemm) and T ensifera Daday T gibberosa Playf and Phormidium articulatum Lyngbyaintermedia Cymbella ventricosa Eunotia arcus Surirella linearis and Closterium parvulum Nag
1 Introduction
Water hyacinth (Eichhornia crassipes) was introduced intothe Nigerian coastal waters in September 1984 from PortoNovo Creek (Benin Republic) and has continued to flourishSchlorin [1] stated that water hyacinth is a sensitive indicatorof environmental status of certain tropical waters Waterhyacinth plant provides suitable surfaces for the developmentof periphyton as well as aquatic fauna on floating leaveshanging roots and creeping stems According to Egborge [2]water hyacinth harbours a variety of organismswhich includealgae rotifers nematodes annelids molluscs hydraceridscladocerans copepod conchostracans isopod amphipodscrabs and fishes Organisms such as snails andmayflies affectthe periphyton species assemblage biomass and productivity[3]
The algae found in water bodies depend on cells whichmay either float on the surface or grow on submerged objects
and are divided into two groups namely phytoplanktonand periphyton [4 5] The term ldquoperiphytonrdquo coined byBehning and Cooke [6 7] was derived from two Greekwords ldquoperirdquo meaning ldquoroundrdquo and ldquophytonrdquomeaning plantPeriphyton has become a universally accepted expressionfor all organisms that are attached to a submerged substrateand generally dominated by photosynthetic organism whichmay be unicellular colonial or filamentous species froma variety of prokaryotic and eukaryotic phyla As appliedto this work Wetzel [8] defined periphyton as the micro-ldquofloralrdquo community living attached to the substrate insidewaterThis microfloral community plays an important role inwater bodies not only by being important primary producers[9 10] and serving as an energy source for higher trophiclevel [11] but also by affecting the nutrient turnover [12]and the transfer of nutrients between the benthic and thepelagic zone [13] Several works on substrate-mediated effecton periphyton biomass and composition have been reported
Hindawi Publishing CorporationJournal of Marine BiologyVolume 2015 Article ID 376986 9 pageshttpdxdoiorg1011552015376986
2 Journal of Marine Biology
Nigeria
(km)0 1 2 4
NPalaver IslandCreeksWater bodies
TownsvillagesEjirin (study area)Lagos State
Vegetation
Ijede
LangbasoBodore
Epe Lagoon
IkosiImode
Oribo Ojidolokun
100100
120 320 520 720 920 1120 1320
120 320 520 720 920 1120 1320
0 60 120 240 360 480
(km)
OceanGulf of Guinea
N
SEW
Palaver Island
Vegetation
Vegetation
Lagos State
Ejirin
Epe
minus100
minus300
minus500
minus700
minus100
minus300
minus500
minus700
Figure 1 Map of Epe Lagoon showing the study area at Ejirin
[14 15] and its usage as an important indicator of the health ofaquatic systems [16ndash18]These organisms are useful indicatorgroups for pollution bioassessment due to their sensitivity topollution Since the composition of periphyton communityon water hyacinth at Ejirin has not been assessed it is there-fore important to document its composition and abundancein relation to environmental characteristics This study willserve as a source of data background and information onwater quality and periphyton abundance and composition
11 Study Area The study site Ejirin (Figure 1) located(6∘8910158401015840N 3∘3810158401015840E) is part of Epe Lagoon freshwater andnontidal lagoon It is sandwiched between Lekki Lagoon tothe east and Lagos Lagoon to the west It experiences thesame hydroclimatic conditions as the rest of southwesternNigeria such that there are two main seasons (wet anddry) The littoral vegetation found there is dominantly Raffiapalm and some dotted mangrove while on surface watersome floating macrophyte like water hyacinth (Eichhorniacrassipes) dominates The people there are mainly artisanalfishermen sand miners and petty traders
2 Materials and Methods
21 Physicochemical Characteristics Water samples were col-lected on each trip between 0900 and 1300 and stored in250mL well labelled plastic bottles and transported to thelaboratory in an ice chest Surface water temperatures were
measured in situ using a mercury-in-glass thermometerand recorded to the nearest 01∘C Transparency was deter-mined using 20 cm white painted Secchi disc while pHvalues were measured using a Graffin digital pH meter Dis-solved oxygen concentration was determined by unmodifiedWinkler method [19] conductivity was assessed using themeter (Philips PW9505) and chemical oxygen demand andbiochemical oxygen demand values were determined usingthe method described in APHA [20] Reactive nitrogenreactive phosphorus sulphate and silicate were measured asdescribed by APHA [20] Rainfall data was obtained from theFederal Meteorological Department Oshodi Lagos
22 Determination of Periphyton Biomass Healthy plantswere carefully selected to ensure uniformity in size beforeputting each into plastic containers with 500mL of tap waterThe attached algae were removed mechanically by shakingvigorously in water as suggested by Foerster and Schlichting[21] and preserved in a well labelled plastic container with4 unbuffered formalin added to fix the periphyton sampleAnother 500mL container was filled with an unfixed samplefor chlorophyll 119886 analysis Chlorophyll 119886 was determined byfluorometric method as described by APHA [20]
23 Analysis of Biological Characteristics Periphyton sampleswere thoroughly investigated using CHA and CHB binocularmicroscope with a calibrated eye piece noting all fieldsCounting was done using a microtransect drop count and
Journal of Marine Biology 3
Table 1 Status of physicochemical parameters at Ejirin part of Epe Lagoon from December 2012 to May 2013
Parameters December January February March April May Mean Standard deviationWater temp (∘C) 293 283 29 306 293 331 2993 172Transparency (cm) 43 57 415 385 34 31 408 911Depth (cm) 25 28 30 27 30 26 277 207pH 6639 615 622 645 66 65 639 017Conductivity (120583scm) 0192 0154 02 0006 02 035 018 011TSS (mgL) 55 66 170 73 1 11 6101 6209TDS (mgL) 065 79 87 141 119 161 9794 5695Rainfall (mm) 132 0 28 501 1653 3408 9957 13225Salinity (permil) 0 0 0 001 0 0 0002 0004Nitrate (mgL) 032 011 008 008 012 007 013 0095Phosphate (mgL) 078 065 059 108 071 059 073 018Sulphate (mgL) 120 080 126 130 121 126 117 019Silicate (mgL) 040 080 011 005 005 006 025 030Periphyton chl a (mgL) 0003 0001 0003 0003 00023 000096Biological oxygen demand (mgL) 48 04 2 37 22 08 232 168Chemical oxygen demand (mgL) 15 16 20 37 32 32 2533 946Dissolved oxygen (mgL) 613 10 45 5 58 6 624 195
10 drops of periphyton samples were investigated for eachmonth as described by [22] All organisms unicels filamentsand coenobia were counted as one and recorded as permL Appropriate texts such as [23ndash26] (Biggs and Kilroy)were used to aid in the identification of periphyton Twocommunity structure parameters were used to determinepossible response of the periphyton flora to environmentalstress These were as follows
(i) Shannon-Wiener diversity index (119867119904) proposed by
Shannon-Wiener in 1963 it is given by
119867119904=
119873 log119873 minus sum119875119894log119875119894
119873
(1)
where 119867119904is Shannon-Wiener index 119873 is the total number
of individuals in the population 119875119894is proportion that the
119894th species represent the total number of individuals in thesampling space sum is summation and 119894 represents countsdenoting 119894th species ranging from 1 to 119899
(ii) Species richness index (119889) proposed by Margalef in1951 it is given by
119889 = 119878 minus
1
In119873 (2)
where 119889 is species richness index 119878 is the number of speciesin the population and119873 is the total number of individuals inspecies
24 Statistical Analysis Statistical analysis was carried outwith the aid of SPSS (version 17) and PAST (version 3)statistical tools Correction coefficient [27] was used to eval-uate relationship between periphyton abundance and someenvironmental variables (temperature salinity total monthly
rainfall TDS TSS transparency pH and micronutrients) Itis given by Spearman rank correlation
119903 = 1 minus [
6sum1198632
119899 (1198992minus 1)
] (3)
where 119903 is the correlation coefficient sum1198632 is the sum ofsquares of difference of the ranks and 119899 is the number ofmonths119905-test analysis was carried out to evaluate statistical
difference (119875 gt 005) in seasonal (wet and dry) abundanceof periphyton community Standard deviation and meananalysis were also evaluated
3 Result
The data for physicochemical features at Ejirin Creek fromDecember 2012 to May 2013 showed seasonal variationas presented in Table 1 Surface water temperature peaked3301∘C in May and lower value of 28∘C in January with amean value of 30∘C The surface water temperature showeda strong significant correlation with rainfall (119903 = 0855lowast 119875 gt005) (Table 3) The surface water pH was acidic throughoutthe sampling period (pH le 66) with a mean value of 639Conductivity peaked 035120583scm in May and lower value of0006120583scm in March with a mean value of 0184 120583scmConductivity showed a strong positive correlation with rain-fall (119903 = 0701) and with periphyton chlorophyll 119886 (119903 =0506) Transparency values were high in the dry monthsand low in the wet months This corresponds to the rainfallpattern encountered during the study The water remainedfresh throughout the study period with salinity value 119878 le001permil
The micronutrients varied throughout the study periodswith reactive nitrate (NO
3-N le 032) reactive phosphate
4 Journal of Marine Biology
Table2Speciesa
bund
ance
distrib
utionof
perip
hytonatEjirin
partof
EpeL
agoo
nfro
mDecem
ber2
012to
May
2013
Perip
hytontaxa
Decem
ber
(Cellsm
Lminus1
)Janu
ary
(Cellsm
Lminus1
)February
(Cellsm
Lminus1
)March
(Cellsm
Lminus1
)Ap
ril(C
ellsm
Lminus1
)May
(Cellsm
Lminus1
)Ph
ylum
Cyano
phyta
ClassCy
anop
hyceae
Order
ICh
roococcales
Chroococcusm
ajor
2447
Chroococcusgardn
eri
2323
Chroococcuso
ccidentalis
28Ch
roococcusd
eltoids
51Ch
roococcusm
ediocris
3337
Chroococcusm
ipita
nensis
36Merism
opediapu
nctata
Meyen
721
Chlorella
subsalaLemm
14Ch
loroglo
eagardneri
23Cy
anothece
sp
14Gom
phosphaeria
sp
22Ap
hanocapsaconferta
4332
Anacystis
sp
14Ap
hanothecec
omasii
22Ap
hanothecev
ariabilis
8Order
IIN
ostocales
Anabaena
spB
oryex
Bornet
4218
3746
Order
IIIOscillatoriales
Lyngbyainterm
ediaAgardhex
Gom
ont
58179
147
201
187
Phormidium
articulatum
4234
Komvophoron
sp
18Ph
ylum
Eug
leno
phyta
ClassEu
glenop
hyceae
Order
IEu
glenales
Eugle
naoxyuris
varcharkowien
sis8
138
11Eu
glena
gracilisK
lebs
12Ph
acus
orbicularis
Hub
ner
14Ph
acus
caud
atus
Hub
ner
13Ph
acus
triqueter
13Trachelomonas
affinis(Lemm)
1212
Trachelomonas
ensiferaDaday
916
Trachelomonas
gibberosaPlayf
1313
Phylum
Bacillarioph
yta
ClassBa
cillario
phyceae
Order
ICentrales
Aulacoseira
granulatavarangustissimafcurvataSimon
172
41301
342
407
524
Aulacoseira
granulatev
arangustissim
afspira
lisOM
ull
181
101
309
498
587
651
Journal of Marine Biology 5Ta
ble2Con
tinued
Perip
hytontaxa
Decem
ber
(Cellsm
Lminus1
)Janu
ary
(Cellsm
Lminus1
)February
(Cellsm
Lminus1
)March
(Cellsm
Lminus1
)Ap
ril(C
ellsm
Lminus1
)May
(Cellsm
Lminus1
)Au
lacoseira
islandica
subspHelv
etica
OM
ull
9840
134
192
271
285
Aulacoseira
granulata(Ehr)
189
115
337
414
541
702
Aulacoseira
italica(Ehr)
1333
103
175
203
198
Hem
idiscus
cuneiform
is29
3521
Cyclo
tella
meneghinianaKu
tzexBr Oslash
7218
108
67Co
cconeis
pediculusE
hr
4862
4898
72Rh
izosolenialongise
ta12
11Rh
izosoleniahebetata
Bail
14Order
IIPennales
Eunotia
arcusE
hr
7237
2737
Diatomatenu
isBo
ry117
121
113
67Cy
mbella
ventric
osaAgardh
3121
2427
34SurirelladebesiTu
rpin
2427
Surirellarobu
stavarsplen
dida
21Surirellarobu
stavararmata
17Surirellalin
earis
Turpin
1947
3827
31Synedraacus
Ehr
2131
Synedraulna
varcontractaEh
r22
1821
38Staurosirellalep
tosta
uron
14Asterio
nella
form
osaHassall
21207
Gyrosig
mascalproidesH
assall
19Gy
rosig
maattenu
atum
Hassall
1613
Gom
phonem
aparvulum
Ehr
2117
2436
31Na
viculalanceolata
Bory
98Na
viculapupu
laKu
tzvarrectangularisGrun
Com
pr
32Na
vicularadiosa
1928
52Na
viculamargalithii
2357
3837
Stauroneisanceps
27Nitzschiaacic
ularisKu
tz
5237
33Nitzschiadissipata
1828
27Nitzschiainterm
edia
3131
3454
4241
Nitzschiainconspicua
3132
3851
Nitzschiaclo
steriu
m31
32Nitzschiagracilis
3129
44Pinn
ulariaacrosphaeria(Breb)v
arm
inor
Kutz
2736
Pinn
ulariagibba
1731
Pseudosta
urosira
brevistria
ta11
AmphoraovalisKu
tz
4752
Epith
emiaargusv
arlongicornisGrun
3919
Epith
emiasorex
47Rh
opalodiaoperculata
(Ehr)Muller
21Ac
hnanthidium
lanceolatum
Kutz
2116
Achn
anthidium
linearis
Kutz
1227
6 Journal of Marine Biology
Table2Con
tinued
Perip
hytontaxa
Decem
ber
(Cellsm
Lminus1
)Janu
ary
(Cellsm
Lminus1
)February
(Cellsm
Lminus1
)March
(Cellsm
Lminus1
)Ap
ril(C
ellsm
Lminus1
)May
(Cellsm
Lminus1
)Ph
ylum
Chlorop
hyta
ClassCh
loroph
yceae
Order
ICh
lorococcales
Ankistrodesmus
falca
tusR
alfsvarmira
bilis
Westflongiseta
Nygaard
29An
kistrodesmus
falca
tusR
alfsvarspirilliform
isWest
32An
kistrodesmus
falca
tusR
alfs
18An
kistrodesmus
falca
tusR
alfsvarsetiformisNygaard
fbrevisNygaard
22An
kistrodesmus
gracilisC
orda
21An
kistrodesmus
braianus
24Scenedesmus
armatus
Chod
at19
2311
13Scenedesmus
perfo
ratesM
eyen
31Scenedesmus
dispar
fcanobe
2-cellu
laire
1114
1222
Scenedesmus
quadric
auda
1119
17Ac
tinastru
mHantzschiiL
agerheim
11Kirchn
eriellaspSchmidle
7Tetra
strum
stauroeniaeform
e16
Tetra
strum
heteracanthu
mfepinep
arcellu
le14
13Selen
astru
mgracile
Reinsch
13Pediastru
msim
plex
Meyen
17Pediastru
mdu
plex
Meyen
17Pediastru
mbiradiatum
varlongico
rnutum
16Pediastru
mtetra
sRalfs
1711
Qua
drigulaclo
sterio
ides
11Crucigeniatetra
pedia(K
irch)W
estetG
S
1417
Crucigeniaminim
aBrun
nthaler
1416
Order
IIZ
ygnematales
Spiro
gyra
spLink
37
Closteriu
mkutzingiifsigmoides
2226
Closteriu
mjen
neriRa
lfs21
Closteriu
mparvulum
Nag
32Staurastrum
pingue
Meyen
exRa
lfs19
18Stau
rastrum
cyclo
canthu
mvarub
acanthum
vuea
picale
2113
Staurodesm
usdickiei
varmaxim
us14
Cosm
arium
spC
orda
exRa
lfs13
Cosm
arium
scottii
18Co
smarium
trachypleu
rum
12Co
smarium
sinostegosv
arobstusiu
s7
Totalspecies
diversity
(119878)
2426
2363
4149
Totalspecies
abun
dance
1169
738
2009
3490
3363
3767
Journal of Marine Biology 7
(PO4-P le 078) silicate (SiO
3le 080) and sulphate (le130)
Periphyton chlorophyll 119886 reached a peak value (0003mgL)recorded in February and April while its lower value(0001mgL) was recorded in March with a mean value of00023mgL Biochemical oxygen demand reached a peakvalue (48mgL) recorded in December and the lowest value(04mgL) was recorded in January with a mean value of2317mgL Chemical oxygen demand value ranged between15mgL (December) and 37mgL (March) with amean valueof 231mgL Dissolved oxygen demand (DO) value reacheda peak value (10mgL) recorded in January and a lower value(45mgL) was recorded in February with a mean value of624mgL
The checklist of the periphyton species between Decem-ber 2012 and May 2013 is presented in Table 2 A total of14 536 individuals of 104 species were recorded throughoutthe study period The total number of taxa varied from 24in December to 26 in January 23 in February 63 in March41 in April and 49 in May Diatom populations during bothseasonswere dominated by 10 centric diatoms and 34 pennatediatoms and a total of 19 species were recorded for Cyanobac-teria Five divisions were recorded with their percent-age of occurrence Bacillariophyta (8269) Cyanobacteria(1043) Chlorophyta (563) and Euglenophyta (115)The total amount of periphyton abundance shows a strongpositive correlation with water temperature (119903 = 0744) pH(119903 = 0797) rainfall (119903 = 0745) and sulphate (119903 = 0707)It also strongly correlates significantly with TDS (119903 = 0836lowast119875 gt 005) and with transparency (119903 = minus0886lowast 119875 gt 005)There was greater species richness during wet months thandry months with a value 119889 le 76 Shannon-Wiener diversityindex value was observed to be119867
119904le 147 (Table 4)
4 Discussion
The range value of the surface water temperature reported isnotable for tropics The highest water temperature observedin May could be a result of time of collection and heatcapacity of waterThe positive correlation that exists betweenrainfall and surface water temperature could explain thepossible effect of precipitation on temperature Nwankwo[28] reported that there are two main seasons in Nigeria dryseason (NovemberndashApril) and wet season (MayndashOctober)The rainy season is ecologically more important in coastalwaters and is bimodal in distribution Floods caused by rain-fall enrich the coastal environmental gradients (horizontaland vertical) With this seasonal pattern it was observedthat transparency total dissolved solids and total suspendedsolids increased with the onset of rainfallThemicronutrientsconcentration level increased as precipitation rate increasedprobably due to input from settlements and wetlands
Odum [29] related pH levels to the amount of carbonatepresent in the water and often considered it an indicator ofthe aquatic chemical environment The observed pH value(pH le 66) falls within the range reported by Nwankwo andAkinsoji [30] for Epe Lagoon The pH value could mainlybe controlled by freshwater swamp exudates that regulate theacidity of the water body Change in pH value has a profound
Table 3 Pearson correlation coefficient matrix of water qualityindices total periphyton abundance and rainfall from December2012 to May 2013 at Ejirin part of Epe Lagoon
ParametersTotal abundance Rainfall
Rainfall 0745 1Water temperature 0744 0855lowast
Transparency minus0886lowast minus0755pH 0797 065Conductivity 0115 0701TSS minus0423 minus0652TDS 0836lowast 0678Salinity 0403 minus0183Reactive nitrate minus0533 minus0375Reactive phosphate 0247 minus0319Sulphate 0707 0374Silicate minus0870lowast minus053Peri chlorophyll a minus0566 minus0007BOD minus0039 minus0398COD 0955lowastlowast 0587DO minus0597 minus0206lowastCorrelation is significant at 005 level (2-tailed)lowastlowastCorrelation is significant at 001 level (2-tailed)
effect on the conductivity level of the water Furthermore thehigh value of dissolved oxygen observed in January could be aresult of combined photosynthetic activity of themicroscopicplants whereas the low value may be attributed to bacterialdegradation of organic matter which was observed at theonset of precipitation
Hynes [31] reported that BOD values of 1-2mgL orless represent clean water of 4ndash7mgL represent slightlypolluted water and of more than 8mgL represent severepollution Therefore based on the above criteria the site wasrelatively clean except for December and March where levelsof contamination were reported The Shannon-Wiener indexof diversity of 1ndash3 according toWilh and Dorris [32] signifiesmoderately polluted water and above 3 signifies clean watersituation In this regard Shannon-Weiner index in Decemberand March in periphyton community may point towardsmoderate pollution at this period
However the chlorophyll 119886 for periphyton communityshowed a rhythmic patternwith nutrient levelmostly reactivenitrate This may explain the importance of reactive nitrateto periphyton community The periphyton abundance in thewet months differs significantly with that of dry months(119905lowast = 8799 119875 gt 005) This could be a result of favourableconditions during this time that resulted in themultiplicationof algal cell and additional input of pennate forms by thefloodsThe algal spectrum observed shows that diatoms werethe dominant species in periphyton community
Bowker and Denny [33] reported the limited growth ofattached diatoms in the dry season and the rapid growth ofmacrophyte tissue This may explain why more species wereobserved on macrophyte tissues in the wet months Some ofthe algae that were common members of the plankton but
8 Journal of Marine Biology
Table 4 Biological indices parameters at Ejirin part of Epe Lagoon from December 2012 to May 2013
Periphyton taxa December January February March April MayTotal species diversity (119878) 24 26 23 63 41 49Total abundance (119873) cellsmLminus1 1169 738 2009 3490 3363 3767Shannon-Wiener index (119867
119904) 117 128 115 147 126 127
Margalef rsquos index (119889) 326 379 289 76 493 583
were found in periphyton community were often trapped bythe roots of the plant like the centric diatoms However thecentric diatoms found in the periphyton community weretransit visitor caught up by the mesh formed of the waterhyacinth roots
The observations that diatoms dominate the periphytoncommunity onwater hyacinth confirm earlier reports [34 35]that diatomsweremore abundant in the algal spectrum of theLagos Lagoon complex
Round [36] observed the abundance of Eunotia sp onLemna roots whereas Bowker and Denny [33] reported thedominance of Achnanthes and Cocconeis sp on the rootsand leaves of Lemna respectively Cocconeis pediculus Ehrand Achnanthidium sp were only found in the periphytoncommunity with Cocconeis occurring all through the monthssuggesting a strong coexistence Cocconeis pediculus Ehroccurred in a range of conditions from clean to moderatelyenriched to much enriched waters Its presence and others(euglenoids blue green algae Nitzschia palea Surirella spPinnularia sp Gomphonema parvulum Mougeotia sp Spir-ogyra sp Trachelomonas affinis (Lemm) T ensifera DadayT gibberosa Playf Phormidium articulatum Lyngbya inter-media Cymbella ventricosa Eunotia arcus Surirella linearisAsterionella formosa Hassall N acicularis Amphora ovalisKutzAnkistrodesmus falcatus Scenedesmus armatusChodatand Closterium parvulum Nag) may suggest pollution byorganic materials
The abundance of periphyton species on the waterhyacinthmay be given a second thought to enhance the aqua-culture production in the area A high species level for bluegreen algae and euglenoids in the periphyton communitymay reveal its suitability in monitoring environmental stressin coastal waters
Conflict of Interests
The authors declare that there is no conflict of interestsregarding the publication of this paper
Acknowledgments
Special thanks are due to the staff of Marine Biology Labo-ratory University of Lagos and Professor D I Nwankwo forthe help throughout the study period
References
[1] H Schlorin ldquoThe water hyacinthmdasha sensitive indicator for theenvironmental status of certain tropical water SCOPEUNEPrdquoSonderband vol 58 pp 217ndash224 1985
[2] A B N Egborge ldquoWater hyacinthmdashbiological museumrdquo inProceedings of the International Workshop on Water Hyacinthpp 52ndash70 Lagos Nigeria August 1988
[3] J W Feminella and C P Hawkins ldquoInteractions betweenstream herbivores and periphyton a quantitative analysis ofpast experimentsrdquo Journal of the North American BenthologicalSociety vol 14 no 4 pp 465ndash509 1995
[4] G E HutchinsonATreatise on Limnology vol 3 of LimnologicaBotany John Wiley amp Sons New York NY USA 1975
[5] J Kalff Limnology Prentice Hall Upper Saddle River NJ USA2002
[6] A L Behning ldquoZur Erforschung der am Flussboden derWolgalebenden OrganismenrdquoMonographien der Biologischen Wolga-Station vol 1 no 1 p 398 1924
[7] W M B Cooke ldquoColonisation of artificial bare areas bymicroorganismsrdquo The Botanical Review vol 22 no 9 pp 613ndash638 1956
[8] R G Wetzel ldquoAttached algal-substrata interactions fact ormyth and when and howrdquo in Periphyton of Freshwater Ecosys-tems R G Wetzel Ed pp 207ndash215 W Junk Publishers TheHague The Netherlands 1983
[9] Y Vadeboncoeur D M Lodge and S R Carpenter ldquoWhole-lake fertilization effects on distribution of primary productionbetween benthic and pelagic habitatsrdquo Ecology vol 82 no 4 pp1065ndash1077 2001
[10] L Liboriussen andE Jeppesen ldquoTemporal dynamics in epipelicpelagic and epiphytic algal production in a clear and a turbidshallow lakerdquo Freshwater Biology vol 48 no 3 pp 418ndash4312003
[11] R E Hecky and R H Hesslein ldquoContributions of benthic algaeto lake food webs as revealed by stable isotope analysisrdquo Journalof the North American Benthological Society vol 14 no 4 pp631ndash653 1995
[12] R G Wetzel ldquoMicrocommunities and microgradients linkingnutrient regenerationmicrobialmutualism and high sustainedaquatic primary productionrdquo Netherlands Journal of AquaticEcology vol 27 no 1 pp 3ndash9 1993
[13] M J Vander Zanden and Y Vadeboncoeur ldquoFishes as integra-tors of benthic and pelagic food webs in lakesrdquo Ecology vol 83no 8 pp 2152ndash2161 2002
[14] D I Nwankwo and A Akinsoji ldquoPeriphyton algae of aeutrophic creek and their possible use as indicatorrdquo NigeriaJournal of Botany vol 1 pp 47ndash54 1998
[15] D I Nwankwo and A O Onitiri ldquoPeriphyton community onsubmerged aquatic macrophytes (horn wort and bladderwort)in Epe Lagoon Nigeriardquo Journal of Agricultural Science andTechnology vol 2 no 2 pp 135ndash141 1992
[16] R L Lowe and Y Pan ldquoBenthic algal communities as biologicalmonitorsrdquo in Algal Ecology Freshwater Benthic Ecosystems RJ Stevenson M L Bothwell and R L Lowe Eds p 753Academic Press San Diego Calif USA 1996
Journal of Marine Biology 9
[17] P V McCormick and R J Stevenson ldquoPeriphyton as a toolfor ecological assessment and management in the FloridaEvergladesrdquo Journal of Phycology vol 34 no 5 pp 726ndash7331998
[18] E E Gaiser D L Childers R D Jones J H Richards L JScinto and J C Trexler ldquoPeriphyton responses to eutrophica-tion in the Florida Everglades cross-system patterns of struc-tural and compositional changerdquo Limnology amp Oceanographyvol 51 no 1 pp 617ndash630 2006
[19] P SWelch LimnologicalMethodsMcGraw-Hill NewYorkNYUSA 1948
[20] APHA Standard Methods for the Examination of Water WasteWater American Public and Health Association AmericanWater Works Association and Water Environment Federation(WEF) 20th edition 1998
[21] J W Foerster and H E Schlichting Jr ldquoPhyco-periphyton in anoligotrophic lakerdquo Transactions of the American MicroscopicalSociety vol 84 no 4 pp 485ndash502 1965
[22] J B Lackey ldquoThe manipulation and counting of river planktonand changes in some organisms due to formalin preservationrdquoUS Public Health Reports vol 53 no 47 pp 2080ndash2093 1938
[23] G M Smith The Fresh-Water Algae of the United StatesMcGraw-Hill London UK 1950
[24] S L VanlandinghamGuide to Identification and EnvironmentalRequirements and Pollution Tolerance of Freshwater Blue-GreenAlgae (Cyanophyta) US Environmental Protection Agency(EPA) 1982
[25] L A Whitford and G H Schmacher A Manual of FreshwaterAlgae Sparks Press Raeigh NC USA 1973
[26] B J F Biggs and C Kilroy Stream Periphyton MonitoringManual NIWA Christchurch New Zealand 2000
[27] A E Ogbeidu Biostatistics A Practical Approach to Researchand Data Handling Mindex Publishing Company LimitedBenin City Nigeria 2005
[28] D I Nwankwo The Microalgae Our Indispensable Allies inAquatic Montoring and Biodiversity Sustainability InauguralLecture Series University of Lagos Press 2004
[29] H T Odum ldquoTrophic structure and productivity of SilverSprings Floridardquo Ecological Monographs vol 27 pp 55ndash1121959
[30] D I Nwankwo andA Akinsoji ldquoEpiphyte community on waterhyacinth Eichhornia crassipes (MART SLOM) in coastal watersof southwestern Nigeriardquo Archiv fur Hydrobiologie vol 124 no4 pp 501ndash511 1992
[31] H B N Hynes The Biology of Polluted Waters LiverpoolUnibersity Press Liverpool UK 1960
[32] J Wilh and T C Dorris ldquoBiological parameters of waterqualityrdquo Bioscience vol 18 pp 477ndash481 1968
[33] D W Bowker and P Denny ldquoThe seasonal succession anddistribution of epiphytic algae in the phyllosphere of Lemnaminor LrdquoArchiv fur Hydrobiologie vol 90 no 1 pp 39ndash55 1980
[34] D I Nwankwo Seasonal changes of phytoplankton of Lagoslagoon and the adjacent sea in relation to environmental factors[PhD thesis] University of Lagos Lagos Nigeria 1984
[35] D I Nwankwo ldquoPhytoplankton of a sewage disposal site inLagos Lagoon Nigeriardquo The Journal of Biological Sciences vol1 no 2 pp 89ndash96 1986
[36] F E RoundTheBiology of Algae Edward Arnold London UK1965
Submit your manuscripts athttpwwwhindawicom
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
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International Journal of
Volume 2014
Zoology
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International Journal of
Microbiology
2 Journal of Marine Biology
Nigeria
(km)0 1 2 4
NPalaver IslandCreeksWater bodies
TownsvillagesEjirin (study area)Lagos State
Vegetation
Ijede
LangbasoBodore
Epe Lagoon
IkosiImode
Oribo Ojidolokun
100100
120 320 520 720 920 1120 1320
120 320 520 720 920 1120 1320
0 60 120 240 360 480
(km)
OceanGulf of Guinea
N
SEW
Palaver Island
Vegetation
Vegetation
Lagos State
Ejirin
Epe
minus100
minus300
minus500
minus700
minus100
minus300
minus500
minus700
Figure 1 Map of Epe Lagoon showing the study area at Ejirin
[14 15] and its usage as an important indicator of the health ofaquatic systems [16ndash18]These organisms are useful indicatorgroups for pollution bioassessment due to their sensitivity topollution Since the composition of periphyton communityon water hyacinth at Ejirin has not been assessed it is there-fore important to document its composition and abundancein relation to environmental characteristics This study willserve as a source of data background and information onwater quality and periphyton abundance and composition
11 Study Area The study site Ejirin (Figure 1) located(6∘8910158401015840N 3∘3810158401015840E) is part of Epe Lagoon freshwater andnontidal lagoon It is sandwiched between Lekki Lagoon tothe east and Lagos Lagoon to the west It experiences thesame hydroclimatic conditions as the rest of southwesternNigeria such that there are two main seasons (wet anddry) The littoral vegetation found there is dominantly Raffiapalm and some dotted mangrove while on surface watersome floating macrophyte like water hyacinth (Eichhorniacrassipes) dominates The people there are mainly artisanalfishermen sand miners and petty traders
2 Materials and Methods
21 Physicochemical Characteristics Water samples were col-lected on each trip between 0900 and 1300 and stored in250mL well labelled plastic bottles and transported to thelaboratory in an ice chest Surface water temperatures were
measured in situ using a mercury-in-glass thermometerand recorded to the nearest 01∘C Transparency was deter-mined using 20 cm white painted Secchi disc while pHvalues were measured using a Graffin digital pH meter Dis-solved oxygen concentration was determined by unmodifiedWinkler method [19] conductivity was assessed using themeter (Philips PW9505) and chemical oxygen demand andbiochemical oxygen demand values were determined usingthe method described in APHA [20] Reactive nitrogenreactive phosphorus sulphate and silicate were measured asdescribed by APHA [20] Rainfall data was obtained from theFederal Meteorological Department Oshodi Lagos
22 Determination of Periphyton Biomass Healthy plantswere carefully selected to ensure uniformity in size beforeputting each into plastic containers with 500mL of tap waterThe attached algae were removed mechanically by shakingvigorously in water as suggested by Foerster and Schlichting[21] and preserved in a well labelled plastic container with4 unbuffered formalin added to fix the periphyton sampleAnother 500mL container was filled with an unfixed samplefor chlorophyll 119886 analysis Chlorophyll 119886 was determined byfluorometric method as described by APHA [20]
23 Analysis of Biological Characteristics Periphyton sampleswere thoroughly investigated using CHA and CHB binocularmicroscope with a calibrated eye piece noting all fieldsCounting was done using a microtransect drop count and
Journal of Marine Biology 3
Table 1 Status of physicochemical parameters at Ejirin part of Epe Lagoon from December 2012 to May 2013
Parameters December January February March April May Mean Standard deviationWater temp (∘C) 293 283 29 306 293 331 2993 172Transparency (cm) 43 57 415 385 34 31 408 911Depth (cm) 25 28 30 27 30 26 277 207pH 6639 615 622 645 66 65 639 017Conductivity (120583scm) 0192 0154 02 0006 02 035 018 011TSS (mgL) 55 66 170 73 1 11 6101 6209TDS (mgL) 065 79 87 141 119 161 9794 5695Rainfall (mm) 132 0 28 501 1653 3408 9957 13225Salinity (permil) 0 0 0 001 0 0 0002 0004Nitrate (mgL) 032 011 008 008 012 007 013 0095Phosphate (mgL) 078 065 059 108 071 059 073 018Sulphate (mgL) 120 080 126 130 121 126 117 019Silicate (mgL) 040 080 011 005 005 006 025 030Periphyton chl a (mgL) 0003 0001 0003 0003 00023 000096Biological oxygen demand (mgL) 48 04 2 37 22 08 232 168Chemical oxygen demand (mgL) 15 16 20 37 32 32 2533 946Dissolved oxygen (mgL) 613 10 45 5 58 6 624 195
10 drops of periphyton samples were investigated for eachmonth as described by [22] All organisms unicels filamentsand coenobia were counted as one and recorded as permL Appropriate texts such as [23ndash26] (Biggs and Kilroy)were used to aid in the identification of periphyton Twocommunity structure parameters were used to determinepossible response of the periphyton flora to environmentalstress These were as follows
(i) Shannon-Wiener diversity index (119867119904) proposed by
Shannon-Wiener in 1963 it is given by
119867119904=
119873 log119873 minus sum119875119894log119875119894
119873
(1)
where 119867119904is Shannon-Wiener index 119873 is the total number
of individuals in the population 119875119894is proportion that the
119894th species represent the total number of individuals in thesampling space sum is summation and 119894 represents countsdenoting 119894th species ranging from 1 to 119899
(ii) Species richness index (119889) proposed by Margalef in1951 it is given by
119889 = 119878 minus
1
In119873 (2)
where 119889 is species richness index 119878 is the number of speciesin the population and119873 is the total number of individuals inspecies
24 Statistical Analysis Statistical analysis was carried outwith the aid of SPSS (version 17) and PAST (version 3)statistical tools Correction coefficient [27] was used to eval-uate relationship between periphyton abundance and someenvironmental variables (temperature salinity total monthly
rainfall TDS TSS transparency pH and micronutrients) Itis given by Spearman rank correlation
119903 = 1 minus [
6sum1198632
119899 (1198992minus 1)
] (3)
where 119903 is the correlation coefficient sum1198632 is the sum ofsquares of difference of the ranks and 119899 is the number ofmonths119905-test analysis was carried out to evaluate statistical
difference (119875 gt 005) in seasonal (wet and dry) abundanceof periphyton community Standard deviation and meananalysis were also evaluated
3 Result
The data for physicochemical features at Ejirin Creek fromDecember 2012 to May 2013 showed seasonal variationas presented in Table 1 Surface water temperature peaked3301∘C in May and lower value of 28∘C in January with amean value of 30∘C The surface water temperature showeda strong significant correlation with rainfall (119903 = 0855lowast 119875 gt005) (Table 3) The surface water pH was acidic throughoutthe sampling period (pH le 66) with a mean value of 639Conductivity peaked 035120583scm in May and lower value of0006120583scm in March with a mean value of 0184 120583scmConductivity showed a strong positive correlation with rain-fall (119903 = 0701) and with periphyton chlorophyll 119886 (119903 =0506) Transparency values were high in the dry monthsand low in the wet months This corresponds to the rainfallpattern encountered during the study The water remainedfresh throughout the study period with salinity value 119878 le001permil
The micronutrients varied throughout the study periodswith reactive nitrate (NO
3-N le 032) reactive phosphate
4 Journal of Marine Biology
Table2Speciesa
bund
ance
distrib
utionof
perip
hytonatEjirin
partof
EpeL
agoo
nfro
mDecem
ber2
012to
May
2013
Perip
hytontaxa
Decem
ber
(Cellsm
Lminus1
)Janu
ary
(Cellsm
Lminus1
)February
(Cellsm
Lminus1
)March
(Cellsm
Lminus1
)Ap
ril(C
ellsm
Lminus1
)May
(Cellsm
Lminus1
)Ph
ylum
Cyano
phyta
ClassCy
anop
hyceae
Order
ICh
roococcales
Chroococcusm
ajor
2447
Chroococcusgardn
eri
2323
Chroococcuso
ccidentalis
28Ch
roococcusd
eltoids
51Ch
roococcusm
ediocris
3337
Chroococcusm
ipita
nensis
36Merism
opediapu
nctata
Meyen
721
Chlorella
subsalaLemm
14Ch
loroglo
eagardneri
23Cy
anothece
sp
14Gom
phosphaeria
sp
22Ap
hanocapsaconferta
4332
Anacystis
sp
14Ap
hanothecec
omasii
22Ap
hanothecev
ariabilis
8Order
IIN
ostocales
Anabaena
spB
oryex
Bornet
4218
3746
Order
IIIOscillatoriales
Lyngbyainterm
ediaAgardhex
Gom
ont
58179
147
201
187
Phormidium
articulatum
4234
Komvophoron
sp
18Ph
ylum
Eug
leno
phyta
ClassEu
glenop
hyceae
Order
IEu
glenales
Eugle
naoxyuris
varcharkowien
sis8
138
11Eu
glena
gracilisK
lebs
12Ph
acus
orbicularis
Hub
ner
14Ph
acus
caud
atus
Hub
ner
13Ph
acus
triqueter
13Trachelomonas
affinis(Lemm)
1212
Trachelomonas
ensiferaDaday
916
Trachelomonas
gibberosaPlayf
1313
Phylum
Bacillarioph
yta
ClassBa
cillario
phyceae
Order
ICentrales
Aulacoseira
granulatavarangustissimafcurvataSimon
172
41301
342
407
524
Aulacoseira
granulatev
arangustissim
afspira
lisOM
ull
181
101
309
498
587
651
Journal of Marine Biology 5Ta
ble2Con
tinued
Perip
hytontaxa
Decem
ber
(Cellsm
Lminus1
)Janu
ary
(Cellsm
Lminus1
)February
(Cellsm
Lminus1
)March
(Cellsm
Lminus1
)Ap
ril(C
ellsm
Lminus1
)May
(Cellsm
Lminus1
)Au
lacoseira
islandica
subspHelv
etica
OM
ull
9840
134
192
271
285
Aulacoseira
granulata(Ehr)
189
115
337
414
541
702
Aulacoseira
italica(Ehr)
1333
103
175
203
198
Hem
idiscus
cuneiform
is29
3521
Cyclo
tella
meneghinianaKu
tzexBr Oslash
7218
108
67Co
cconeis
pediculusE
hr
4862
4898
72Rh
izosolenialongise
ta12
11Rh
izosoleniahebetata
Bail
14Order
IIPennales
Eunotia
arcusE
hr
7237
2737
Diatomatenu
isBo
ry117
121
113
67Cy
mbella
ventric
osaAgardh
3121
2427
34SurirelladebesiTu
rpin
2427
Surirellarobu
stavarsplen
dida
21Surirellarobu
stavararmata
17Surirellalin
earis
Turpin
1947
3827
31Synedraacus
Ehr
2131
Synedraulna
varcontractaEh
r22
1821
38Staurosirellalep
tosta
uron
14Asterio
nella
form
osaHassall
21207
Gyrosig
mascalproidesH
assall
19Gy
rosig
maattenu
atum
Hassall
1613
Gom
phonem
aparvulum
Ehr
2117
2436
31Na
viculalanceolata
Bory
98Na
viculapupu
laKu
tzvarrectangularisGrun
Com
pr
32Na
vicularadiosa
1928
52Na
viculamargalithii
2357
3837
Stauroneisanceps
27Nitzschiaacic
ularisKu
tz
5237
33Nitzschiadissipata
1828
27Nitzschiainterm
edia
3131
3454
4241
Nitzschiainconspicua
3132
3851
Nitzschiaclo
steriu
m31
32Nitzschiagracilis
3129
44Pinn
ulariaacrosphaeria(Breb)v
arm
inor
Kutz
2736
Pinn
ulariagibba
1731
Pseudosta
urosira
brevistria
ta11
AmphoraovalisKu
tz
4752
Epith
emiaargusv
arlongicornisGrun
3919
Epith
emiasorex
47Rh
opalodiaoperculata
(Ehr)Muller
21Ac
hnanthidium
lanceolatum
Kutz
2116
Achn
anthidium
linearis
Kutz
1227
6 Journal of Marine Biology
Table2Con
tinued
Perip
hytontaxa
Decem
ber
(Cellsm
Lminus1
)Janu
ary
(Cellsm
Lminus1
)February
(Cellsm
Lminus1
)March
(Cellsm
Lminus1
)Ap
ril(C
ellsm
Lminus1
)May
(Cellsm
Lminus1
)Ph
ylum
Chlorop
hyta
ClassCh
loroph
yceae
Order
ICh
lorococcales
Ankistrodesmus
falca
tusR
alfsvarmira
bilis
Westflongiseta
Nygaard
29An
kistrodesmus
falca
tusR
alfsvarspirilliform
isWest
32An
kistrodesmus
falca
tusR
alfs
18An
kistrodesmus
falca
tusR
alfsvarsetiformisNygaard
fbrevisNygaard
22An
kistrodesmus
gracilisC
orda
21An
kistrodesmus
braianus
24Scenedesmus
armatus
Chod
at19
2311
13Scenedesmus
perfo
ratesM
eyen
31Scenedesmus
dispar
fcanobe
2-cellu
laire
1114
1222
Scenedesmus
quadric
auda
1119
17Ac
tinastru
mHantzschiiL
agerheim
11Kirchn
eriellaspSchmidle
7Tetra
strum
stauroeniaeform
e16
Tetra
strum
heteracanthu
mfepinep
arcellu
le14
13Selen
astru
mgracile
Reinsch
13Pediastru
msim
plex
Meyen
17Pediastru
mdu
plex
Meyen
17Pediastru
mbiradiatum
varlongico
rnutum
16Pediastru
mtetra
sRalfs
1711
Qua
drigulaclo
sterio
ides
11Crucigeniatetra
pedia(K
irch)W
estetG
S
1417
Crucigeniaminim
aBrun
nthaler
1416
Order
IIZ
ygnematales
Spiro
gyra
spLink
37
Closteriu
mkutzingiifsigmoides
2226
Closteriu
mjen
neriRa
lfs21
Closteriu
mparvulum
Nag
32Staurastrum
pingue
Meyen
exRa
lfs19
18Stau
rastrum
cyclo
canthu
mvarub
acanthum
vuea
picale
2113
Staurodesm
usdickiei
varmaxim
us14
Cosm
arium
spC
orda
exRa
lfs13
Cosm
arium
scottii
18Co
smarium
trachypleu
rum
12Co
smarium
sinostegosv
arobstusiu
s7
Totalspecies
diversity
(119878)
2426
2363
4149
Totalspecies
abun
dance
1169
738
2009
3490
3363
3767
Journal of Marine Biology 7
(PO4-P le 078) silicate (SiO
3le 080) and sulphate (le130)
Periphyton chlorophyll 119886 reached a peak value (0003mgL)recorded in February and April while its lower value(0001mgL) was recorded in March with a mean value of00023mgL Biochemical oxygen demand reached a peakvalue (48mgL) recorded in December and the lowest value(04mgL) was recorded in January with a mean value of2317mgL Chemical oxygen demand value ranged between15mgL (December) and 37mgL (March) with amean valueof 231mgL Dissolved oxygen demand (DO) value reacheda peak value (10mgL) recorded in January and a lower value(45mgL) was recorded in February with a mean value of624mgL
The checklist of the periphyton species between Decem-ber 2012 and May 2013 is presented in Table 2 A total of14 536 individuals of 104 species were recorded throughoutthe study period The total number of taxa varied from 24in December to 26 in January 23 in February 63 in March41 in April and 49 in May Diatom populations during bothseasonswere dominated by 10 centric diatoms and 34 pennatediatoms and a total of 19 species were recorded for Cyanobac-teria Five divisions were recorded with their percent-age of occurrence Bacillariophyta (8269) Cyanobacteria(1043) Chlorophyta (563) and Euglenophyta (115)The total amount of periphyton abundance shows a strongpositive correlation with water temperature (119903 = 0744) pH(119903 = 0797) rainfall (119903 = 0745) and sulphate (119903 = 0707)It also strongly correlates significantly with TDS (119903 = 0836lowast119875 gt 005) and with transparency (119903 = minus0886lowast 119875 gt 005)There was greater species richness during wet months thandry months with a value 119889 le 76 Shannon-Wiener diversityindex value was observed to be119867
119904le 147 (Table 4)
4 Discussion
The range value of the surface water temperature reported isnotable for tropics The highest water temperature observedin May could be a result of time of collection and heatcapacity of waterThe positive correlation that exists betweenrainfall and surface water temperature could explain thepossible effect of precipitation on temperature Nwankwo[28] reported that there are two main seasons in Nigeria dryseason (NovemberndashApril) and wet season (MayndashOctober)The rainy season is ecologically more important in coastalwaters and is bimodal in distribution Floods caused by rain-fall enrich the coastal environmental gradients (horizontaland vertical) With this seasonal pattern it was observedthat transparency total dissolved solids and total suspendedsolids increased with the onset of rainfallThemicronutrientsconcentration level increased as precipitation rate increasedprobably due to input from settlements and wetlands
Odum [29] related pH levels to the amount of carbonatepresent in the water and often considered it an indicator ofthe aquatic chemical environment The observed pH value(pH le 66) falls within the range reported by Nwankwo andAkinsoji [30] for Epe Lagoon The pH value could mainlybe controlled by freshwater swamp exudates that regulate theacidity of the water body Change in pH value has a profound
Table 3 Pearson correlation coefficient matrix of water qualityindices total periphyton abundance and rainfall from December2012 to May 2013 at Ejirin part of Epe Lagoon
ParametersTotal abundance Rainfall
Rainfall 0745 1Water temperature 0744 0855lowast
Transparency minus0886lowast minus0755pH 0797 065Conductivity 0115 0701TSS minus0423 minus0652TDS 0836lowast 0678Salinity 0403 minus0183Reactive nitrate minus0533 minus0375Reactive phosphate 0247 minus0319Sulphate 0707 0374Silicate minus0870lowast minus053Peri chlorophyll a minus0566 minus0007BOD minus0039 minus0398COD 0955lowastlowast 0587DO minus0597 minus0206lowastCorrelation is significant at 005 level (2-tailed)lowastlowastCorrelation is significant at 001 level (2-tailed)
effect on the conductivity level of the water Furthermore thehigh value of dissolved oxygen observed in January could be aresult of combined photosynthetic activity of themicroscopicplants whereas the low value may be attributed to bacterialdegradation of organic matter which was observed at theonset of precipitation
Hynes [31] reported that BOD values of 1-2mgL orless represent clean water of 4ndash7mgL represent slightlypolluted water and of more than 8mgL represent severepollution Therefore based on the above criteria the site wasrelatively clean except for December and March where levelsof contamination were reported The Shannon-Wiener indexof diversity of 1ndash3 according toWilh and Dorris [32] signifiesmoderately polluted water and above 3 signifies clean watersituation In this regard Shannon-Weiner index in Decemberand March in periphyton community may point towardsmoderate pollution at this period
However the chlorophyll 119886 for periphyton communityshowed a rhythmic patternwith nutrient levelmostly reactivenitrate This may explain the importance of reactive nitrateto periphyton community The periphyton abundance in thewet months differs significantly with that of dry months(119905lowast = 8799 119875 gt 005) This could be a result of favourableconditions during this time that resulted in themultiplicationof algal cell and additional input of pennate forms by thefloodsThe algal spectrum observed shows that diatoms werethe dominant species in periphyton community
Bowker and Denny [33] reported the limited growth ofattached diatoms in the dry season and the rapid growth ofmacrophyte tissue This may explain why more species wereobserved on macrophyte tissues in the wet months Some ofthe algae that were common members of the plankton but
8 Journal of Marine Biology
Table 4 Biological indices parameters at Ejirin part of Epe Lagoon from December 2012 to May 2013
Periphyton taxa December January February March April MayTotal species diversity (119878) 24 26 23 63 41 49Total abundance (119873) cellsmLminus1 1169 738 2009 3490 3363 3767Shannon-Wiener index (119867
119904) 117 128 115 147 126 127
Margalef rsquos index (119889) 326 379 289 76 493 583
were found in periphyton community were often trapped bythe roots of the plant like the centric diatoms However thecentric diatoms found in the periphyton community weretransit visitor caught up by the mesh formed of the waterhyacinth roots
The observations that diatoms dominate the periphytoncommunity onwater hyacinth confirm earlier reports [34 35]that diatomsweremore abundant in the algal spectrum of theLagos Lagoon complex
Round [36] observed the abundance of Eunotia sp onLemna roots whereas Bowker and Denny [33] reported thedominance of Achnanthes and Cocconeis sp on the rootsand leaves of Lemna respectively Cocconeis pediculus Ehrand Achnanthidium sp were only found in the periphytoncommunity with Cocconeis occurring all through the monthssuggesting a strong coexistence Cocconeis pediculus Ehroccurred in a range of conditions from clean to moderatelyenriched to much enriched waters Its presence and others(euglenoids blue green algae Nitzschia palea Surirella spPinnularia sp Gomphonema parvulum Mougeotia sp Spir-ogyra sp Trachelomonas affinis (Lemm) T ensifera DadayT gibberosa Playf Phormidium articulatum Lyngbya inter-media Cymbella ventricosa Eunotia arcus Surirella linearisAsterionella formosa Hassall N acicularis Amphora ovalisKutzAnkistrodesmus falcatus Scenedesmus armatusChodatand Closterium parvulum Nag) may suggest pollution byorganic materials
The abundance of periphyton species on the waterhyacinthmay be given a second thought to enhance the aqua-culture production in the area A high species level for bluegreen algae and euglenoids in the periphyton communitymay reveal its suitability in monitoring environmental stressin coastal waters
Conflict of Interests
The authors declare that there is no conflict of interestsregarding the publication of this paper
Acknowledgments
Special thanks are due to the staff of Marine Biology Labo-ratory University of Lagos and Professor D I Nwankwo forthe help throughout the study period
References
[1] H Schlorin ldquoThe water hyacinthmdasha sensitive indicator for theenvironmental status of certain tropical water SCOPEUNEPrdquoSonderband vol 58 pp 217ndash224 1985
[2] A B N Egborge ldquoWater hyacinthmdashbiological museumrdquo inProceedings of the International Workshop on Water Hyacinthpp 52ndash70 Lagos Nigeria August 1988
[3] J W Feminella and C P Hawkins ldquoInteractions betweenstream herbivores and periphyton a quantitative analysis ofpast experimentsrdquo Journal of the North American BenthologicalSociety vol 14 no 4 pp 465ndash509 1995
[4] G E HutchinsonATreatise on Limnology vol 3 of LimnologicaBotany John Wiley amp Sons New York NY USA 1975
[5] J Kalff Limnology Prentice Hall Upper Saddle River NJ USA2002
[6] A L Behning ldquoZur Erforschung der am Flussboden derWolgalebenden OrganismenrdquoMonographien der Biologischen Wolga-Station vol 1 no 1 p 398 1924
[7] W M B Cooke ldquoColonisation of artificial bare areas bymicroorganismsrdquo The Botanical Review vol 22 no 9 pp 613ndash638 1956
[8] R G Wetzel ldquoAttached algal-substrata interactions fact ormyth and when and howrdquo in Periphyton of Freshwater Ecosys-tems R G Wetzel Ed pp 207ndash215 W Junk Publishers TheHague The Netherlands 1983
[9] Y Vadeboncoeur D M Lodge and S R Carpenter ldquoWhole-lake fertilization effects on distribution of primary productionbetween benthic and pelagic habitatsrdquo Ecology vol 82 no 4 pp1065ndash1077 2001
[10] L Liboriussen andE Jeppesen ldquoTemporal dynamics in epipelicpelagic and epiphytic algal production in a clear and a turbidshallow lakerdquo Freshwater Biology vol 48 no 3 pp 418ndash4312003
[11] R E Hecky and R H Hesslein ldquoContributions of benthic algaeto lake food webs as revealed by stable isotope analysisrdquo Journalof the North American Benthological Society vol 14 no 4 pp631ndash653 1995
[12] R G Wetzel ldquoMicrocommunities and microgradients linkingnutrient regenerationmicrobialmutualism and high sustainedaquatic primary productionrdquo Netherlands Journal of AquaticEcology vol 27 no 1 pp 3ndash9 1993
[13] M J Vander Zanden and Y Vadeboncoeur ldquoFishes as integra-tors of benthic and pelagic food webs in lakesrdquo Ecology vol 83no 8 pp 2152ndash2161 2002
[14] D I Nwankwo and A Akinsoji ldquoPeriphyton algae of aeutrophic creek and their possible use as indicatorrdquo NigeriaJournal of Botany vol 1 pp 47ndash54 1998
[15] D I Nwankwo and A O Onitiri ldquoPeriphyton community onsubmerged aquatic macrophytes (horn wort and bladderwort)in Epe Lagoon Nigeriardquo Journal of Agricultural Science andTechnology vol 2 no 2 pp 135ndash141 1992
[16] R L Lowe and Y Pan ldquoBenthic algal communities as biologicalmonitorsrdquo in Algal Ecology Freshwater Benthic Ecosystems RJ Stevenson M L Bothwell and R L Lowe Eds p 753Academic Press San Diego Calif USA 1996
Journal of Marine Biology 9
[17] P V McCormick and R J Stevenson ldquoPeriphyton as a toolfor ecological assessment and management in the FloridaEvergladesrdquo Journal of Phycology vol 34 no 5 pp 726ndash7331998
[18] E E Gaiser D L Childers R D Jones J H Richards L JScinto and J C Trexler ldquoPeriphyton responses to eutrophica-tion in the Florida Everglades cross-system patterns of struc-tural and compositional changerdquo Limnology amp Oceanographyvol 51 no 1 pp 617ndash630 2006
[19] P SWelch LimnologicalMethodsMcGraw-Hill NewYorkNYUSA 1948
[20] APHA Standard Methods for the Examination of Water WasteWater American Public and Health Association AmericanWater Works Association and Water Environment Federation(WEF) 20th edition 1998
[21] J W Foerster and H E Schlichting Jr ldquoPhyco-periphyton in anoligotrophic lakerdquo Transactions of the American MicroscopicalSociety vol 84 no 4 pp 485ndash502 1965
[22] J B Lackey ldquoThe manipulation and counting of river planktonand changes in some organisms due to formalin preservationrdquoUS Public Health Reports vol 53 no 47 pp 2080ndash2093 1938
[23] G M Smith The Fresh-Water Algae of the United StatesMcGraw-Hill London UK 1950
[24] S L VanlandinghamGuide to Identification and EnvironmentalRequirements and Pollution Tolerance of Freshwater Blue-GreenAlgae (Cyanophyta) US Environmental Protection Agency(EPA) 1982
[25] L A Whitford and G H Schmacher A Manual of FreshwaterAlgae Sparks Press Raeigh NC USA 1973
[26] B J F Biggs and C Kilroy Stream Periphyton MonitoringManual NIWA Christchurch New Zealand 2000
[27] A E Ogbeidu Biostatistics A Practical Approach to Researchand Data Handling Mindex Publishing Company LimitedBenin City Nigeria 2005
[28] D I Nwankwo The Microalgae Our Indispensable Allies inAquatic Montoring and Biodiversity Sustainability InauguralLecture Series University of Lagos Press 2004
[29] H T Odum ldquoTrophic structure and productivity of SilverSprings Floridardquo Ecological Monographs vol 27 pp 55ndash1121959
[30] D I Nwankwo andA Akinsoji ldquoEpiphyte community on waterhyacinth Eichhornia crassipes (MART SLOM) in coastal watersof southwestern Nigeriardquo Archiv fur Hydrobiologie vol 124 no4 pp 501ndash511 1992
[31] H B N Hynes The Biology of Polluted Waters LiverpoolUnibersity Press Liverpool UK 1960
[32] J Wilh and T C Dorris ldquoBiological parameters of waterqualityrdquo Bioscience vol 18 pp 477ndash481 1968
[33] D W Bowker and P Denny ldquoThe seasonal succession anddistribution of epiphytic algae in the phyllosphere of Lemnaminor LrdquoArchiv fur Hydrobiologie vol 90 no 1 pp 39ndash55 1980
[34] D I Nwankwo Seasonal changes of phytoplankton of Lagoslagoon and the adjacent sea in relation to environmental factors[PhD thesis] University of Lagos Lagos Nigeria 1984
[35] D I Nwankwo ldquoPhytoplankton of a sewage disposal site inLagos Lagoon Nigeriardquo The Journal of Biological Sciences vol1 no 2 pp 89ndash96 1986
[36] F E RoundTheBiology of Algae Edward Arnold London UK1965
Submit your manuscripts athttpwwwhindawicom
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
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International Journal of
Volume 2014
Zoology
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Signal TransductionJournal of
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ArchaeaHindawi Publishing Corporationhttpwwwhindawicom Volume 2014
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Nucleic AcidsJournal of
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Enzyme Research
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
International Journal of
Microbiology
Journal of Marine Biology 3
Table 1 Status of physicochemical parameters at Ejirin part of Epe Lagoon from December 2012 to May 2013
Parameters December January February March April May Mean Standard deviationWater temp (∘C) 293 283 29 306 293 331 2993 172Transparency (cm) 43 57 415 385 34 31 408 911Depth (cm) 25 28 30 27 30 26 277 207pH 6639 615 622 645 66 65 639 017Conductivity (120583scm) 0192 0154 02 0006 02 035 018 011TSS (mgL) 55 66 170 73 1 11 6101 6209TDS (mgL) 065 79 87 141 119 161 9794 5695Rainfall (mm) 132 0 28 501 1653 3408 9957 13225Salinity (permil) 0 0 0 001 0 0 0002 0004Nitrate (mgL) 032 011 008 008 012 007 013 0095Phosphate (mgL) 078 065 059 108 071 059 073 018Sulphate (mgL) 120 080 126 130 121 126 117 019Silicate (mgL) 040 080 011 005 005 006 025 030Periphyton chl a (mgL) 0003 0001 0003 0003 00023 000096Biological oxygen demand (mgL) 48 04 2 37 22 08 232 168Chemical oxygen demand (mgL) 15 16 20 37 32 32 2533 946Dissolved oxygen (mgL) 613 10 45 5 58 6 624 195
10 drops of periphyton samples were investigated for eachmonth as described by [22] All organisms unicels filamentsand coenobia were counted as one and recorded as permL Appropriate texts such as [23ndash26] (Biggs and Kilroy)were used to aid in the identification of periphyton Twocommunity structure parameters were used to determinepossible response of the periphyton flora to environmentalstress These were as follows
(i) Shannon-Wiener diversity index (119867119904) proposed by
Shannon-Wiener in 1963 it is given by
119867119904=
119873 log119873 minus sum119875119894log119875119894
119873
(1)
where 119867119904is Shannon-Wiener index 119873 is the total number
of individuals in the population 119875119894is proportion that the
119894th species represent the total number of individuals in thesampling space sum is summation and 119894 represents countsdenoting 119894th species ranging from 1 to 119899
(ii) Species richness index (119889) proposed by Margalef in1951 it is given by
119889 = 119878 minus
1
In119873 (2)
where 119889 is species richness index 119878 is the number of speciesin the population and119873 is the total number of individuals inspecies
24 Statistical Analysis Statistical analysis was carried outwith the aid of SPSS (version 17) and PAST (version 3)statistical tools Correction coefficient [27] was used to eval-uate relationship between periphyton abundance and someenvironmental variables (temperature salinity total monthly
rainfall TDS TSS transparency pH and micronutrients) Itis given by Spearman rank correlation
119903 = 1 minus [
6sum1198632
119899 (1198992minus 1)
] (3)
where 119903 is the correlation coefficient sum1198632 is the sum ofsquares of difference of the ranks and 119899 is the number ofmonths119905-test analysis was carried out to evaluate statistical
difference (119875 gt 005) in seasonal (wet and dry) abundanceof periphyton community Standard deviation and meananalysis were also evaluated
3 Result
The data for physicochemical features at Ejirin Creek fromDecember 2012 to May 2013 showed seasonal variationas presented in Table 1 Surface water temperature peaked3301∘C in May and lower value of 28∘C in January with amean value of 30∘C The surface water temperature showeda strong significant correlation with rainfall (119903 = 0855lowast 119875 gt005) (Table 3) The surface water pH was acidic throughoutthe sampling period (pH le 66) with a mean value of 639Conductivity peaked 035120583scm in May and lower value of0006120583scm in March with a mean value of 0184 120583scmConductivity showed a strong positive correlation with rain-fall (119903 = 0701) and with periphyton chlorophyll 119886 (119903 =0506) Transparency values were high in the dry monthsand low in the wet months This corresponds to the rainfallpattern encountered during the study The water remainedfresh throughout the study period with salinity value 119878 le001permil
The micronutrients varied throughout the study periodswith reactive nitrate (NO
3-N le 032) reactive phosphate
4 Journal of Marine Biology
Table2Speciesa
bund
ance
distrib
utionof
perip
hytonatEjirin
partof
EpeL
agoo
nfro
mDecem
ber2
012to
May
2013
Perip
hytontaxa
Decem
ber
(Cellsm
Lminus1
)Janu
ary
(Cellsm
Lminus1
)February
(Cellsm
Lminus1
)March
(Cellsm
Lminus1
)Ap
ril(C
ellsm
Lminus1
)May
(Cellsm
Lminus1
)Ph
ylum
Cyano
phyta
ClassCy
anop
hyceae
Order
ICh
roococcales
Chroococcusm
ajor
2447
Chroococcusgardn
eri
2323
Chroococcuso
ccidentalis
28Ch
roococcusd
eltoids
51Ch
roococcusm
ediocris
3337
Chroococcusm
ipita
nensis
36Merism
opediapu
nctata
Meyen
721
Chlorella
subsalaLemm
14Ch
loroglo
eagardneri
23Cy
anothece
sp
14Gom
phosphaeria
sp
22Ap
hanocapsaconferta
4332
Anacystis
sp
14Ap
hanothecec
omasii
22Ap
hanothecev
ariabilis
8Order
IIN
ostocales
Anabaena
spB
oryex
Bornet
4218
3746
Order
IIIOscillatoriales
Lyngbyainterm
ediaAgardhex
Gom
ont
58179
147
201
187
Phormidium
articulatum
4234
Komvophoron
sp
18Ph
ylum
Eug
leno
phyta
ClassEu
glenop
hyceae
Order
IEu
glenales
Eugle
naoxyuris
varcharkowien
sis8
138
11Eu
glena
gracilisK
lebs
12Ph
acus
orbicularis
Hub
ner
14Ph
acus
caud
atus
Hub
ner
13Ph
acus
triqueter
13Trachelomonas
affinis(Lemm)
1212
Trachelomonas
ensiferaDaday
916
Trachelomonas
gibberosaPlayf
1313
Phylum
Bacillarioph
yta
ClassBa
cillario
phyceae
Order
ICentrales
Aulacoseira
granulatavarangustissimafcurvataSimon
172
41301
342
407
524
Aulacoseira
granulatev
arangustissim
afspira
lisOM
ull
181
101
309
498
587
651
Journal of Marine Biology 5Ta
ble2Con
tinued
Perip
hytontaxa
Decem
ber
(Cellsm
Lminus1
)Janu
ary
(Cellsm
Lminus1
)February
(Cellsm
Lminus1
)March
(Cellsm
Lminus1
)Ap
ril(C
ellsm
Lminus1
)May
(Cellsm
Lminus1
)Au
lacoseira
islandica
subspHelv
etica
OM
ull
9840
134
192
271
285
Aulacoseira
granulata(Ehr)
189
115
337
414
541
702
Aulacoseira
italica(Ehr)
1333
103
175
203
198
Hem
idiscus
cuneiform
is29
3521
Cyclo
tella
meneghinianaKu
tzexBr Oslash
7218
108
67Co
cconeis
pediculusE
hr
4862
4898
72Rh
izosolenialongise
ta12
11Rh
izosoleniahebetata
Bail
14Order
IIPennales
Eunotia
arcusE
hr
7237
2737
Diatomatenu
isBo
ry117
121
113
67Cy
mbella
ventric
osaAgardh
3121
2427
34SurirelladebesiTu
rpin
2427
Surirellarobu
stavarsplen
dida
21Surirellarobu
stavararmata
17Surirellalin
earis
Turpin
1947
3827
31Synedraacus
Ehr
2131
Synedraulna
varcontractaEh
r22
1821
38Staurosirellalep
tosta
uron
14Asterio
nella
form
osaHassall
21207
Gyrosig
mascalproidesH
assall
19Gy
rosig
maattenu
atum
Hassall
1613
Gom
phonem
aparvulum
Ehr
2117
2436
31Na
viculalanceolata
Bory
98Na
viculapupu
laKu
tzvarrectangularisGrun
Com
pr
32Na
vicularadiosa
1928
52Na
viculamargalithii
2357
3837
Stauroneisanceps
27Nitzschiaacic
ularisKu
tz
5237
33Nitzschiadissipata
1828
27Nitzschiainterm
edia
3131
3454
4241
Nitzschiainconspicua
3132
3851
Nitzschiaclo
steriu
m31
32Nitzschiagracilis
3129
44Pinn
ulariaacrosphaeria(Breb)v
arm
inor
Kutz
2736
Pinn
ulariagibba
1731
Pseudosta
urosira
brevistria
ta11
AmphoraovalisKu
tz
4752
Epith
emiaargusv
arlongicornisGrun
3919
Epith
emiasorex
47Rh
opalodiaoperculata
(Ehr)Muller
21Ac
hnanthidium
lanceolatum
Kutz
2116
Achn
anthidium
linearis
Kutz
1227
6 Journal of Marine Biology
Table2Con
tinued
Perip
hytontaxa
Decem
ber
(Cellsm
Lminus1
)Janu
ary
(Cellsm
Lminus1
)February
(Cellsm
Lminus1
)March
(Cellsm
Lminus1
)Ap
ril(C
ellsm
Lminus1
)May
(Cellsm
Lminus1
)Ph
ylum
Chlorop
hyta
ClassCh
loroph
yceae
Order
ICh
lorococcales
Ankistrodesmus
falca
tusR
alfsvarmira
bilis
Westflongiseta
Nygaard
29An
kistrodesmus
falca
tusR
alfsvarspirilliform
isWest
32An
kistrodesmus
falca
tusR
alfs
18An
kistrodesmus
falca
tusR
alfsvarsetiformisNygaard
fbrevisNygaard
22An
kistrodesmus
gracilisC
orda
21An
kistrodesmus
braianus
24Scenedesmus
armatus
Chod
at19
2311
13Scenedesmus
perfo
ratesM
eyen
31Scenedesmus
dispar
fcanobe
2-cellu
laire
1114
1222
Scenedesmus
quadric
auda
1119
17Ac
tinastru
mHantzschiiL
agerheim
11Kirchn
eriellaspSchmidle
7Tetra
strum
stauroeniaeform
e16
Tetra
strum
heteracanthu
mfepinep
arcellu
le14
13Selen
astru
mgracile
Reinsch
13Pediastru
msim
plex
Meyen
17Pediastru
mdu
plex
Meyen
17Pediastru
mbiradiatum
varlongico
rnutum
16Pediastru
mtetra
sRalfs
1711
Qua
drigulaclo
sterio
ides
11Crucigeniatetra
pedia(K
irch)W
estetG
S
1417
Crucigeniaminim
aBrun
nthaler
1416
Order
IIZ
ygnematales
Spiro
gyra
spLink
37
Closteriu
mkutzingiifsigmoides
2226
Closteriu
mjen
neriRa
lfs21
Closteriu
mparvulum
Nag
32Staurastrum
pingue
Meyen
exRa
lfs19
18Stau
rastrum
cyclo
canthu
mvarub
acanthum
vuea
picale
2113
Staurodesm
usdickiei
varmaxim
us14
Cosm
arium
spC
orda
exRa
lfs13
Cosm
arium
scottii
18Co
smarium
trachypleu
rum
12Co
smarium
sinostegosv
arobstusiu
s7
Totalspecies
diversity
(119878)
2426
2363
4149
Totalspecies
abun
dance
1169
738
2009
3490
3363
3767
Journal of Marine Biology 7
(PO4-P le 078) silicate (SiO
3le 080) and sulphate (le130)
Periphyton chlorophyll 119886 reached a peak value (0003mgL)recorded in February and April while its lower value(0001mgL) was recorded in March with a mean value of00023mgL Biochemical oxygen demand reached a peakvalue (48mgL) recorded in December and the lowest value(04mgL) was recorded in January with a mean value of2317mgL Chemical oxygen demand value ranged between15mgL (December) and 37mgL (March) with amean valueof 231mgL Dissolved oxygen demand (DO) value reacheda peak value (10mgL) recorded in January and a lower value(45mgL) was recorded in February with a mean value of624mgL
The checklist of the periphyton species between Decem-ber 2012 and May 2013 is presented in Table 2 A total of14 536 individuals of 104 species were recorded throughoutthe study period The total number of taxa varied from 24in December to 26 in January 23 in February 63 in March41 in April and 49 in May Diatom populations during bothseasonswere dominated by 10 centric diatoms and 34 pennatediatoms and a total of 19 species were recorded for Cyanobac-teria Five divisions were recorded with their percent-age of occurrence Bacillariophyta (8269) Cyanobacteria(1043) Chlorophyta (563) and Euglenophyta (115)The total amount of periphyton abundance shows a strongpositive correlation with water temperature (119903 = 0744) pH(119903 = 0797) rainfall (119903 = 0745) and sulphate (119903 = 0707)It also strongly correlates significantly with TDS (119903 = 0836lowast119875 gt 005) and with transparency (119903 = minus0886lowast 119875 gt 005)There was greater species richness during wet months thandry months with a value 119889 le 76 Shannon-Wiener diversityindex value was observed to be119867
119904le 147 (Table 4)
4 Discussion
The range value of the surface water temperature reported isnotable for tropics The highest water temperature observedin May could be a result of time of collection and heatcapacity of waterThe positive correlation that exists betweenrainfall and surface water temperature could explain thepossible effect of precipitation on temperature Nwankwo[28] reported that there are two main seasons in Nigeria dryseason (NovemberndashApril) and wet season (MayndashOctober)The rainy season is ecologically more important in coastalwaters and is bimodal in distribution Floods caused by rain-fall enrich the coastal environmental gradients (horizontaland vertical) With this seasonal pattern it was observedthat transparency total dissolved solids and total suspendedsolids increased with the onset of rainfallThemicronutrientsconcentration level increased as precipitation rate increasedprobably due to input from settlements and wetlands
Odum [29] related pH levels to the amount of carbonatepresent in the water and often considered it an indicator ofthe aquatic chemical environment The observed pH value(pH le 66) falls within the range reported by Nwankwo andAkinsoji [30] for Epe Lagoon The pH value could mainlybe controlled by freshwater swamp exudates that regulate theacidity of the water body Change in pH value has a profound
Table 3 Pearson correlation coefficient matrix of water qualityindices total periphyton abundance and rainfall from December2012 to May 2013 at Ejirin part of Epe Lagoon
ParametersTotal abundance Rainfall
Rainfall 0745 1Water temperature 0744 0855lowast
Transparency minus0886lowast minus0755pH 0797 065Conductivity 0115 0701TSS minus0423 minus0652TDS 0836lowast 0678Salinity 0403 minus0183Reactive nitrate minus0533 minus0375Reactive phosphate 0247 minus0319Sulphate 0707 0374Silicate minus0870lowast minus053Peri chlorophyll a minus0566 minus0007BOD minus0039 minus0398COD 0955lowastlowast 0587DO minus0597 minus0206lowastCorrelation is significant at 005 level (2-tailed)lowastlowastCorrelation is significant at 001 level (2-tailed)
effect on the conductivity level of the water Furthermore thehigh value of dissolved oxygen observed in January could be aresult of combined photosynthetic activity of themicroscopicplants whereas the low value may be attributed to bacterialdegradation of organic matter which was observed at theonset of precipitation
Hynes [31] reported that BOD values of 1-2mgL orless represent clean water of 4ndash7mgL represent slightlypolluted water and of more than 8mgL represent severepollution Therefore based on the above criteria the site wasrelatively clean except for December and March where levelsof contamination were reported The Shannon-Wiener indexof diversity of 1ndash3 according toWilh and Dorris [32] signifiesmoderately polluted water and above 3 signifies clean watersituation In this regard Shannon-Weiner index in Decemberand March in periphyton community may point towardsmoderate pollution at this period
However the chlorophyll 119886 for periphyton communityshowed a rhythmic patternwith nutrient levelmostly reactivenitrate This may explain the importance of reactive nitrateto periphyton community The periphyton abundance in thewet months differs significantly with that of dry months(119905lowast = 8799 119875 gt 005) This could be a result of favourableconditions during this time that resulted in themultiplicationof algal cell and additional input of pennate forms by thefloodsThe algal spectrum observed shows that diatoms werethe dominant species in periphyton community
Bowker and Denny [33] reported the limited growth ofattached diatoms in the dry season and the rapid growth ofmacrophyte tissue This may explain why more species wereobserved on macrophyte tissues in the wet months Some ofthe algae that were common members of the plankton but
8 Journal of Marine Biology
Table 4 Biological indices parameters at Ejirin part of Epe Lagoon from December 2012 to May 2013
Periphyton taxa December January February March April MayTotal species diversity (119878) 24 26 23 63 41 49Total abundance (119873) cellsmLminus1 1169 738 2009 3490 3363 3767Shannon-Wiener index (119867
119904) 117 128 115 147 126 127
Margalef rsquos index (119889) 326 379 289 76 493 583
were found in periphyton community were often trapped bythe roots of the plant like the centric diatoms However thecentric diatoms found in the periphyton community weretransit visitor caught up by the mesh formed of the waterhyacinth roots
The observations that diatoms dominate the periphytoncommunity onwater hyacinth confirm earlier reports [34 35]that diatomsweremore abundant in the algal spectrum of theLagos Lagoon complex
Round [36] observed the abundance of Eunotia sp onLemna roots whereas Bowker and Denny [33] reported thedominance of Achnanthes and Cocconeis sp on the rootsand leaves of Lemna respectively Cocconeis pediculus Ehrand Achnanthidium sp were only found in the periphytoncommunity with Cocconeis occurring all through the monthssuggesting a strong coexistence Cocconeis pediculus Ehroccurred in a range of conditions from clean to moderatelyenriched to much enriched waters Its presence and others(euglenoids blue green algae Nitzschia palea Surirella spPinnularia sp Gomphonema parvulum Mougeotia sp Spir-ogyra sp Trachelomonas affinis (Lemm) T ensifera DadayT gibberosa Playf Phormidium articulatum Lyngbya inter-media Cymbella ventricosa Eunotia arcus Surirella linearisAsterionella formosa Hassall N acicularis Amphora ovalisKutzAnkistrodesmus falcatus Scenedesmus armatusChodatand Closterium parvulum Nag) may suggest pollution byorganic materials
The abundance of periphyton species on the waterhyacinthmay be given a second thought to enhance the aqua-culture production in the area A high species level for bluegreen algae and euglenoids in the periphyton communitymay reveal its suitability in monitoring environmental stressin coastal waters
Conflict of Interests
The authors declare that there is no conflict of interestsregarding the publication of this paper
Acknowledgments
Special thanks are due to the staff of Marine Biology Labo-ratory University of Lagos and Professor D I Nwankwo forthe help throughout the study period
References
[1] H Schlorin ldquoThe water hyacinthmdasha sensitive indicator for theenvironmental status of certain tropical water SCOPEUNEPrdquoSonderband vol 58 pp 217ndash224 1985
[2] A B N Egborge ldquoWater hyacinthmdashbiological museumrdquo inProceedings of the International Workshop on Water Hyacinthpp 52ndash70 Lagos Nigeria August 1988
[3] J W Feminella and C P Hawkins ldquoInteractions betweenstream herbivores and periphyton a quantitative analysis ofpast experimentsrdquo Journal of the North American BenthologicalSociety vol 14 no 4 pp 465ndash509 1995
[4] G E HutchinsonATreatise on Limnology vol 3 of LimnologicaBotany John Wiley amp Sons New York NY USA 1975
[5] J Kalff Limnology Prentice Hall Upper Saddle River NJ USA2002
[6] A L Behning ldquoZur Erforschung der am Flussboden derWolgalebenden OrganismenrdquoMonographien der Biologischen Wolga-Station vol 1 no 1 p 398 1924
[7] W M B Cooke ldquoColonisation of artificial bare areas bymicroorganismsrdquo The Botanical Review vol 22 no 9 pp 613ndash638 1956
[8] R G Wetzel ldquoAttached algal-substrata interactions fact ormyth and when and howrdquo in Periphyton of Freshwater Ecosys-tems R G Wetzel Ed pp 207ndash215 W Junk Publishers TheHague The Netherlands 1983
[9] Y Vadeboncoeur D M Lodge and S R Carpenter ldquoWhole-lake fertilization effects on distribution of primary productionbetween benthic and pelagic habitatsrdquo Ecology vol 82 no 4 pp1065ndash1077 2001
[10] L Liboriussen andE Jeppesen ldquoTemporal dynamics in epipelicpelagic and epiphytic algal production in a clear and a turbidshallow lakerdquo Freshwater Biology vol 48 no 3 pp 418ndash4312003
[11] R E Hecky and R H Hesslein ldquoContributions of benthic algaeto lake food webs as revealed by stable isotope analysisrdquo Journalof the North American Benthological Society vol 14 no 4 pp631ndash653 1995
[12] R G Wetzel ldquoMicrocommunities and microgradients linkingnutrient regenerationmicrobialmutualism and high sustainedaquatic primary productionrdquo Netherlands Journal of AquaticEcology vol 27 no 1 pp 3ndash9 1993
[13] M J Vander Zanden and Y Vadeboncoeur ldquoFishes as integra-tors of benthic and pelagic food webs in lakesrdquo Ecology vol 83no 8 pp 2152ndash2161 2002
[14] D I Nwankwo and A Akinsoji ldquoPeriphyton algae of aeutrophic creek and their possible use as indicatorrdquo NigeriaJournal of Botany vol 1 pp 47ndash54 1998
[15] D I Nwankwo and A O Onitiri ldquoPeriphyton community onsubmerged aquatic macrophytes (horn wort and bladderwort)in Epe Lagoon Nigeriardquo Journal of Agricultural Science andTechnology vol 2 no 2 pp 135ndash141 1992
[16] R L Lowe and Y Pan ldquoBenthic algal communities as biologicalmonitorsrdquo in Algal Ecology Freshwater Benthic Ecosystems RJ Stevenson M L Bothwell and R L Lowe Eds p 753Academic Press San Diego Calif USA 1996
Journal of Marine Biology 9
[17] P V McCormick and R J Stevenson ldquoPeriphyton as a toolfor ecological assessment and management in the FloridaEvergladesrdquo Journal of Phycology vol 34 no 5 pp 726ndash7331998
[18] E E Gaiser D L Childers R D Jones J H Richards L JScinto and J C Trexler ldquoPeriphyton responses to eutrophica-tion in the Florida Everglades cross-system patterns of struc-tural and compositional changerdquo Limnology amp Oceanographyvol 51 no 1 pp 617ndash630 2006
[19] P SWelch LimnologicalMethodsMcGraw-Hill NewYorkNYUSA 1948
[20] APHA Standard Methods for the Examination of Water WasteWater American Public and Health Association AmericanWater Works Association and Water Environment Federation(WEF) 20th edition 1998
[21] J W Foerster and H E Schlichting Jr ldquoPhyco-periphyton in anoligotrophic lakerdquo Transactions of the American MicroscopicalSociety vol 84 no 4 pp 485ndash502 1965
[22] J B Lackey ldquoThe manipulation and counting of river planktonand changes in some organisms due to formalin preservationrdquoUS Public Health Reports vol 53 no 47 pp 2080ndash2093 1938
[23] G M Smith The Fresh-Water Algae of the United StatesMcGraw-Hill London UK 1950
[24] S L VanlandinghamGuide to Identification and EnvironmentalRequirements and Pollution Tolerance of Freshwater Blue-GreenAlgae (Cyanophyta) US Environmental Protection Agency(EPA) 1982
[25] L A Whitford and G H Schmacher A Manual of FreshwaterAlgae Sparks Press Raeigh NC USA 1973
[26] B J F Biggs and C Kilroy Stream Periphyton MonitoringManual NIWA Christchurch New Zealand 2000
[27] A E Ogbeidu Biostatistics A Practical Approach to Researchand Data Handling Mindex Publishing Company LimitedBenin City Nigeria 2005
[28] D I Nwankwo The Microalgae Our Indispensable Allies inAquatic Montoring and Biodiversity Sustainability InauguralLecture Series University of Lagos Press 2004
[29] H T Odum ldquoTrophic structure and productivity of SilverSprings Floridardquo Ecological Monographs vol 27 pp 55ndash1121959
[30] D I Nwankwo andA Akinsoji ldquoEpiphyte community on waterhyacinth Eichhornia crassipes (MART SLOM) in coastal watersof southwestern Nigeriardquo Archiv fur Hydrobiologie vol 124 no4 pp 501ndash511 1992
[31] H B N Hynes The Biology of Polluted Waters LiverpoolUnibersity Press Liverpool UK 1960
[32] J Wilh and T C Dorris ldquoBiological parameters of waterqualityrdquo Bioscience vol 18 pp 477ndash481 1968
[33] D W Bowker and P Denny ldquoThe seasonal succession anddistribution of epiphytic algae in the phyllosphere of Lemnaminor LrdquoArchiv fur Hydrobiologie vol 90 no 1 pp 39ndash55 1980
[34] D I Nwankwo Seasonal changes of phytoplankton of Lagoslagoon and the adjacent sea in relation to environmental factors[PhD thesis] University of Lagos Lagos Nigeria 1984
[35] D I Nwankwo ldquoPhytoplankton of a sewage disposal site inLagos Lagoon Nigeriardquo The Journal of Biological Sciences vol1 no 2 pp 89ndash96 1986
[36] F E RoundTheBiology of Algae Edward Arnold London UK1965
Submit your manuscripts athttpwwwhindawicom
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
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Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
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International Journal of
Volume 2014
Zoology
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Molecular Biology International
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Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Signal TransductionJournal of
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Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
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ArchaeaHindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
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Enzyme Research
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
International Journal of
Microbiology
4 Journal of Marine Biology
Table2Speciesa
bund
ance
distrib
utionof
perip
hytonatEjirin
partof
EpeL
agoo
nfro
mDecem
ber2
012to
May
2013
Perip
hytontaxa
Decem
ber
(Cellsm
Lminus1
)Janu
ary
(Cellsm
Lminus1
)February
(Cellsm
Lminus1
)March
(Cellsm
Lminus1
)Ap
ril(C
ellsm
Lminus1
)May
(Cellsm
Lminus1
)Ph
ylum
Cyano
phyta
ClassCy
anop
hyceae
Order
ICh
roococcales
Chroococcusm
ajor
2447
Chroococcusgardn
eri
2323
Chroococcuso
ccidentalis
28Ch
roococcusd
eltoids
51Ch
roococcusm
ediocris
3337
Chroococcusm
ipita
nensis
36Merism
opediapu
nctata
Meyen
721
Chlorella
subsalaLemm
14Ch
loroglo
eagardneri
23Cy
anothece
sp
14Gom
phosphaeria
sp
22Ap
hanocapsaconferta
4332
Anacystis
sp
14Ap
hanothecec
omasii
22Ap
hanothecev
ariabilis
8Order
IIN
ostocales
Anabaena
spB
oryex
Bornet
4218
3746
Order
IIIOscillatoriales
Lyngbyainterm
ediaAgardhex
Gom
ont
58179
147
201
187
Phormidium
articulatum
4234
Komvophoron
sp
18Ph
ylum
Eug
leno
phyta
ClassEu
glenop
hyceae
Order
IEu
glenales
Eugle
naoxyuris
varcharkowien
sis8
138
11Eu
glena
gracilisK
lebs
12Ph
acus
orbicularis
Hub
ner
14Ph
acus
caud
atus
Hub
ner
13Ph
acus
triqueter
13Trachelomonas
affinis(Lemm)
1212
Trachelomonas
ensiferaDaday
916
Trachelomonas
gibberosaPlayf
1313
Phylum
Bacillarioph
yta
ClassBa
cillario
phyceae
Order
ICentrales
Aulacoseira
granulatavarangustissimafcurvataSimon
172
41301
342
407
524
Aulacoseira
granulatev
arangustissim
afspira
lisOM
ull
181
101
309
498
587
651
Journal of Marine Biology 5Ta
ble2Con
tinued
Perip
hytontaxa
Decem
ber
(Cellsm
Lminus1
)Janu
ary
(Cellsm
Lminus1
)February
(Cellsm
Lminus1
)March
(Cellsm
Lminus1
)Ap
ril(C
ellsm
Lminus1
)May
(Cellsm
Lminus1
)Au
lacoseira
islandica
subspHelv
etica
OM
ull
9840
134
192
271
285
Aulacoseira
granulata(Ehr)
189
115
337
414
541
702
Aulacoseira
italica(Ehr)
1333
103
175
203
198
Hem
idiscus
cuneiform
is29
3521
Cyclo
tella
meneghinianaKu
tzexBr Oslash
7218
108
67Co
cconeis
pediculusE
hr
4862
4898
72Rh
izosolenialongise
ta12
11Rh
izosoleniahebetata
Bail
14Order
IIPennales
Eunotia
arcusE
hr
7237
2737
Diatomatenu
isBo
ry117
121
113
67Cy
mbella
ventric
osaAgardh
3121
2427
34SurirelladebesiTu
rpin
2427
Surirellarobu
stavarsplen
dida
21Surirellarobu
stavararmata
17Surirellalin
earis
Turpin
1947
3827
31Synedraacus
Ehr
2131
Synedraulna
varcontractaEh
r22
1821
38Staurosirellalep
tosta
uron
14Asterio
nella
form
osaHassall
21207
Gyrosig
mascalproidesH
assall
19Gy
rosig
maattenu
atum
Hassall
1613
Gom
phonem
aparvulum
Ehr
2117
2436
31Na
viculalanceolata
Bory
98Na
viculapupu
laKu
tzvarrectangularisGrun
Com
pr
32Na
vicularadiosa
1928
52Na
viculamargalithii
2357
3837
Stauroneisanceps
27Nitzschiaacic
ularisKu
tz
5237
33Nitzschiadissipata
1828
27Nitzschiainterm
edia
3131
3454
4241
Nitzschiainconspicua
3132
3851
Nitzschiaclo
steriu
m31
32Nitzschiagracilis
3129
44Pinn
ulariaacrosphaeria(Breb)v
arm
inor
Kutz
2736
Pinn
ulariagibba
1731
Pseudosta
urosira
brevistria
ta11
AmphoraovalisKu
tz
4752
Epith
emiaargusv
arlongicornisGrun
3919
Epith
emiasorex
47Rh
opalodiaoperculata
(Ehr)Muller
21Ac
hnanthidium
lanceolatum
Kutz
2116
Achn
anthidium
linearis
Kutz
1227
6 Journal of Marine Biology
Table2Con
tinued
Perip
hytontaxa
Decem
ber
(Cellsm
Lminus1
)Janu
ary
(Cellsm
Lminus1
)February
(Cellsm
Lminus1
)March
(Cellsm
Lminus1
)Ap
ril(C
ellsm
Lminus1
)May
(Cellsm
Lminus1
)Ph
ylum
Chlorop
hyta
ClassCh
loroph
yceae
Order
ICh
lorococcales
Ankistrodesmus
falca
tusR
alfsvarmira
bilis
Westflongiseta
Nygaard
29An
kistrodesmus
falca
tusR
alfsvarspirilliform
isWest
32An
kistrodesmus
falca
tusR
alfs
18An
kistrodesmus
falca
tusR
alfsvarsetiformisNygaard
fbrevisNygaard
22An
kistrodesmus
gracilisC
orda
21An
kistrodesmus
braianus
24Scenedesmus
armatus
Chod
at19
2311
13Scenedesmus
perfo
ratesM
eyen
31Scenedesmus
dispar
fcanobe
2-cellu
laire
1114
1222
Scenedesmus
quadric
auda
1119
17Ac
tinastru
mHantzschiiL
agerheim
11Kirchn
eriellaspSchmidle
7Tetra
strum
stauroeniaeform
e16
Tetra
strum
heteracanthu
mfepinep
arcellu
le14
13Selen
astru
mgracile
Reinsch
13Pediastru
msim
plex
Meyen
17Pediastru
mdu
plex
Meyen
17Pediastru
mbiradiatum
varlongico
rnutum
16Pediastru
mtetra
sRalfs
1711
Qua
drigulaclo
sterio
ides
11Crucigeniatetra
pedia(K
irch)W
estetG
S
1417
Crucigeniaminim
aBrun
nthaler
1416
Order
IIZ
ygnematales
Spiro
gyra
spLink
37
Closteriu
mkutzingiifsigmoides
2226
Closteriu
mjen
neriRa
lfs21
Closteriu
mparvulum
Nag
32Staurastrum
pingue
Meyen
exRa
lfs19
18Stau
rastrum
cyclo
canthu
mvarub
acanthum
vuea
picale
2113
Staurodesm
usdickiei
varmaxim
us14
Cosm
arium
spC
orda
exRa
lfs13
Cosm
arium
scottii
18Co
smarium
trachypleu
rum
12Co
smarium
sinostegosv
arobstusiu
s7
Totalspecies
diversity
(119878)
2426
2363
4149
Totalspecies
abun
dance
1169
738
2009
3490
3363
3767
Journal of Marine Biology 7
(PO4-P le 078) silicate (SiO
3le 080) and sulphate (le130)
Periphyton chlorophyll 119886 reached a peak value (0003mgL)recorded in February and April while its lower value(0001mgL) was recorded in March with a mean value of00023mgL Biochemical oxygen demand reached a peakvalue (48mgL) recorded in December and the lowest value(04mgL) was recorded in January with a mean value of2317mgL Chemical oxygen demand value ranged between15mgL (December) and 37mgL (March) with amean valueof 231mgL Dissolved oxygen demand (DO) value reacheda peak value (10mgL) recorded in January and a lower value(45mgL) was recorded in February with a mean value of624mgL
The checklist of the periphyton species between Decem-ber 2012 and May 2013 is presented in Table 2 A total of14 536 individuals of 104 species were recorded throughoutthe study period The total number of taxa varied from 24in December to 26 in January 23 in February 63 in March41 in April and 49 in May Diatom populations during bothseasonswere dominated by 10 centric diatoms and 34 pennatediatoms and a total of 19 species were recorded for Cyanobac-teria Five divisions were recorded with their percent-age of occurrence Bacillariophyta (8269) Cyanobacteria(1043) Chlorophyta (563) and Euglenophyta (115)The total amount of periphyton abundance shows a strongpositive correlation with water temperature (119903 = 0744) pH(119903 = 0797) rainfall (119903 = 0745) and sulphate (119903 = 0707)It also strongly correlates significantly with TDS (119903 = 0836lowast119875 gt 005) and with transparency (119903 = minus0886lowast 119875 gt 005)There was greater species richness during wet months thandry months with a value 119889 le 76 Shannon-Wiener diversityindex value was observed to be119867
119904le 147 (Table 4)
4 Discussion
The range value of the surface water temperature reported isnotable for tropics The highest water temperature observedin May could be a result of time of collection and heatcapacity of waterThe positive correlation that exists betweenrainfall and surface water temperature could explain thepossible effect of precipitation on temperature Nwankwo[28] reported that there are two main seasons in Nigeria dryseason (NovemberndashApril) and wet season (MayndashOctober)The rainy season is ecologically more important in coastalwaters and is bimodal in distribution Floods caused by rain-fall enrich the coastal environmental gradients (horizontaland vertical) With this seasonal pattern it was observedthat transparency total dissolved solids and total suspendedsolids increased with the onset of rainfallThemicronutrientsconcentration level increased as precipitation rate increasedprobably due to input from settlements and wetlands
Odum [29] related pH levels to the amount of carbonatepresent in the water and often considered it an indicator ofthe aquatic chemical environment The observed pH value(pH le 66) falls within the range reported by Nwankwo andAkinsoji [30] for Epe Lagoon The pH value could mainlybe controlled by freshwater swamp exudates that regulate theacidity of the water body Change in pH value has a profound
Table 3 Pearson correlation coefficient matrix of water qualityindices total periphyton abundance and rainfall from December2012 to May 2013 at Ejirin part of Epe Lagoon
ParametersTotal abundance Rainfall
Rainfall 0745 1Water temperature 0744 0855lowast
Transparency minus0886lowast minus0755pH 0797 065Conductivity 0115 0701TSS minus0423 minus0652TDS 0836lowast 0678Salinity 0403 minus0183Reactive nitrate minus0533 minus0375Reactive phosphate 0247 minus0319Sulphate 0707 0374Silicate minus0870lowast minus053Peri chlorophyll a minus0566 minus0007BOD minus0039 minus0398COD 0955lowastlowast 0587DO minus0597 minus0206lowastCorrelation is significant at 005 level (2-tailed)lowastlowastCorrelation is significant at 001 level (2-tailed)
effect on the conductivity level of the water Furthermore thehigh value of dissolved oxygen observed in January could be aresult of combined photosynthetic activity of themicroscopicplants whereas the low value may be attributed to bacterialdegradation of organic matter which was observed at theonset of precipitation
Hynes [31] reported that BOD values of 1-2mgL orless represent clean water of 4ndash7mgL represent slightlypolluted water and of more than 8mgL represent severepollution Therefore based on the above criteria the site wasrelatively clean except for December and March where levelsof contamination were reported The Shannon-Wiener indexof diversity of 1ndash3 according toWilh and Dorris [32] signifiesmoderately polluted water and above 3 signifies clean watersituation In this regard Shannon-Weiner index in Decemberand March in periphyton community may point towardsmoderate pollution at this period
However the chlorophyll 119886 for periphyton communityshowed a rhythmic patternwith nutrient levelmostly reactivenitrate This may explain the importance of reactive nitrateto periphyton community The periphyton abundance in thewet months differs significantly with that of dry months(119905lowast = 8799 119875 gt 005) This could be a result of favourableconditions during this time that resulted in themultiplicationof algal cell and additional input of pennate forms by thefloodsThe algal spectrum observed shows that diatoms werethe dominant species in periphyton community
Bowker and Denny [33] reported the limited growth ofattached diatoms in the dry season and the rapid growth ofmacrophyte tissue This may explain why more species wereobserved on macrophyte tissues in the wet months Some ofthe algae that were common members of the plankton but
8 Journal of Marine Biology
Table 4 Biological indices parameters at Ejirin part of Epe Lagoon from December 2012 to May 2013
Periphyton taxa December January February March April MayTotal species diversity (119878) 24 26 23 63 41 49Total abundance (119873) cellsmLminus1 1169 738 2009 3490 3363 3767Shannon-Wiener index (119867
119904) 117 128 115 147 126 127
Margalef rsquos index (119889) 326 379 289 76 493 583
were found in periphyton community were often trapped bythe roots of the plant like the centric diatoms However thecentric diatoms found in the periphyton community weretransit visitor caught up by the mesh formed of the waterhyacinth roots
The observations that diatoms dominate the periphytoncommunity onwater hyacinth confirm earlier reports [34 35]that diatomsweremore abundant in the algal spectrum of theLagos Lagoon complex
Round [36] observed the abundance of Eunotia sp onLemna roots whereas Bowker and Denny [33] reported thedominance of Achnanthes and Cocconeis sp on the rootsand leaves of Lemna respectively Cocconeis pediculus Ehrand Achnanthidium sp were only found in the periphytoncommunity with Cocconeis occurring all through the monthssuggesting a strong coexistence Cocconeis pediculus Ehroccurred in a range of conditions from clean to moderatelyenriched to much enriched waters Its presence and others(euglenoids blue green algae Nitzschia palea Surirella spPinnularia sp Gomphonema parvulum Mougeotia sp Spir-ogyra sp Trachelomonas affinis (Lemm) T ensifera DadayT gibberosa Playf Phormidium articulatum Lyngbya inter-media Cymbella ventricosa Eunotia arcus Surirella linearisAsterionella formosa Hassall N acicularis Amphora ovalisKutzAnkistrodesmus falcatus Scenedesmus armatusChodatand Closterium parvulum Nag) may suggest pollution byorganic materials
The abundance of periphyton species on the waterhyacinthmay be given a second thought to enhance the aqua-culture production in the area A high species level for bluegreen algae and euglenoids in the periphyton communitymay reveal its suitability in monitoring environmental stressin coastal waters
Conflict of Interests
The authors declare that there is no conflict of interestsregarding the publication of this paper
Acknowledgments
Special thanks are due to the staff of Marine Biology Labo-ratory University of Lagos and Professor D I Nwankwo forthe help throughout the study period
References
[1] H Schlorin ldquoThe water hyacinthmdasha sensitive indicator for theenvironmental status of certain tropical water SCOPEUNEPrdquoSonderband vol 58 pp 217ndash224 1985
[2] A B N Egborge ldquoWater hyacinthmdashbiological museumrdquo inProceedings of the International Workshop on Water Hyacinthpp 52ndash70 Lagos Nigeria August 1988
[3] J W Feminella and C P Hawkins ldquoInteractions betweenstream herbivores and periphyton a quantitative analysis ofpast experimentsrdquo Journal of the North American BenthologicalSociety vol 14 no 4 pp 465ndash509 1995
[4] G E HutchinsonATreatise on Limnology vol 3 of LimnologicaBotany John Wiley amp Sons New York NY USA 1975
[5] J Kalff Limnology Prentice Hall Upper Saddle River NJ USA2002
[6] A L Behning ldquoZur Erforschung der am Flussboden derWolgalebenden OrganismenrdquoMonographien der Biologischen Wolga-Station vol 1 no 1 p 398 1924
[7] W M B Cooke ldquoColonisation of artificial bare areas bymicroorganismsrdquo The Botanical Review vol 22 no 9 pp 613ndash638 1956
[8] R G Wetzel ldquoAttached algal-substrata interactions fact ormyth and when and howrdquo in Periphyton of Freshwater Ecosys-tems R G Wetzel Ed pp 207ndash215 W Junk Publishers TheHague The Netherlands 1983
[9] Y Vadeboncoeur D M Lodge and S R Carpenter ldquoWhole-lake fertilization effects on distribution of primary productionbetween benthic and pelagic habitatsrdquo Ecology vol 82 no 4 pp1065ndash1077 2001
[10] L Liboriussen andE Jeppesen ldquoTemporal dynamics in epipelicpelagic and epiphytic algal production in a clear and a turbidshallow lakerdquo Freshwater Biology vol 48 no 3 pp 418ndash4312003
[11] R E Hecky and R H Hesslein ldquoContributions of benthic algaeto lake food webs as revealed by stable isotope analysisrdquo Journalof the North American Benthological Society vol 14 no 4 pp631ndash653 1995
[12] R G Wetzel ldquoMicrocommunities and microgradients linkingnutrient regenerationmicrobialmutualism and high sustainedaquatic primary productionrdquo Netherlands Journal of AquaticEcology vol 27 no 1 pp 3ndash9 1993
[13] M J Vander Zanden and Y Vadeboncoeur ldquoFishes as integra-tors of benthic and pelagic food webs in lakesrdquo Ecology vol 83no 8 pp 2152ndash2161 2002
[14] D I Nwankwo and A Akinsoji ldquoPeriphyton algae of aeutrophic creek and their possible use as indicatorrdquo NigeriaJournal of Botany vol 1 pp 47ndash54 1998
[15] D I Nwankwo and A O Onitiri ldquoPeriphyton community onsubmerged aquatic macrophytes (horn wort and bladderwort)in Epe Lagoon Nigeriardquo Journal of Agricultural Science andTechnology vol 2 no 2 pp 135ndash141 1992
[16] R L Lowe and Y Pan ldquoBenthic algal communities as biologicalmonitorsrdquo in Algal Ecology Freshwater Benthic Ecosystems RJ Stevenson M L Bothwell and R L Lowe Eds p 753Academic Press San Diego Calif USA 1996
Journal of Marine Biology 9
[17] P V McCormick and R J Stevenson ldquoPeriphyton as a toolfor ecological assessment and management in the FloridaEvergladesrdquo Journal of Phycology vol 34 no 5 pp 726ndash7331998
[18] E E Gaiser D L Childers R D Jones J H Richards L JScinto and J C Trexler ldquoPeriphyton responses to eutrophica-tion in the Florida Everglades cross-system patterns of struc-tural and compositional changerdquo Limnology amp Oceanographyvol 51 no 1 pp 617ndash630 2006
[19] P SWelch LimnologicalMethodsMcGraw-Hill NewYorkNYUSA 1948
[20] APHA Standard Methods for the Examination of Water WasteWater American Public and Health Association AmericanWater Works Association and Water Environment Federation(WEF) 20th edition 1998
[21] J W Foerster and H E Schlichting Jr ldquoPhyco-periphyton in anoligotrophic lakerdquo Transactions of the American MicroscopicalSociety vol 84 no 4 pp 485ndash502 1965
[22] J B Lackey ldquoThe manipulation and counting of river planktonand changes in some organisms due to formalin preservationrdquoUS Public Health Reports vol 53 no 47 pp 2080ndash2093 1938
[23] G M Smith The Fresh-Water Algae of the United StatesMcGraw-Hill London UK 1950
[24] S L VanlandinghamGuide to Identification and EnvironmentalRequirements and Pollution Tolerance of Freshwater Blue-GreenAlgae (Cyanophyta) US Environmental Protection Agency(EPA) 1982
[25] L A Whitford and G H Schmacher A Manual of FreshwaterAlgae Sparks Press Raeigh NC USA 1973
[26] B J F Biggs and C Kilroy Stream Periphyton MonitoringManual NIWA Christchurch New Zealand 2000
[27] A E Ogbeidu Biostatistics A Practical Approach to Researchand Data Handling Mindex Publishing Company LimitedBenin City Nigeria 2005
[28] D I Nwankwo The Microalgae Our Indispensable Allies inAquatic Montoring and Biodiversity Sustainability InauguralLecture Series University of Lagos Press 2004
[29] H T Odum ldquoTrophic structure and productivity of SilverSprings Floridardquo Ecological Monographs vol 27 pp 55ndash1121959
[30] D I Nwankwo andA Akinsoji ldquoEpiphyte community on waterhyacinth Eichhornia crassipes (MART SLOM) in coastal watersof southwestern Nigeriardquo Archiv fur Hydrobiologie vol 124 no4 pp 501ndash511 1992
[31] H B N Hynes The Biology of Polluted Waters LiverpoolUnibersity Press Liverpool UK 1960
[32] J Wilh and T C Dorris ldquoBiological parameters of waterqualityrdquo Bioscience vol 18 pp 477ndash481 1968
[33] D W Bowker and P Denny ldquoThe seasonal succession anddistribution of epiphytic algae in the phyllosphere of Lemnaminor LrdquoArchiv fur Hydrobiologie vol 90 no 1 pp 39ndash55 1980
[34] D I Nwankwo Seasonal changes of phytoplankton of Lagoslagoon and the adjacent sea in relation to environmental factors[PhD thesis] University of Lagos Lagos Nigeria 1984
[35] D I Nwankwo ldquoPhytoplankton of a sewage disposal site inLagos Lagoon Nigeriardquo The Journal of Biological Sciences vol1 no 2 pp 89ndash96 1986
[36] F E RoundTheBiology of Algae Edward Arnold London UK1965
Submit your manuscripts athttpwwwhindawicom
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Anatomy Research International
PeptidesInternational Journal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporation httpwwwhindawicom
International Journal of
Volume 2014
Zoology
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Molecular Biology International
GenomicsInternational Journal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
The Scientific World JournalHindawi Publishing Corporation httpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
BioinformaticsAdvances in
Marine BiologyJournal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Signal TransductionJournal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
BioMed Research International
Evolutionary BiologyInternational Journal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Biochemistry Research International
ArchaeaHindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Genetics Research International
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Advances in
Virolog y
Hindawi Publishing Corporationhttpwwwhindawicom
Nucleic AcidsJournal of
Volume 2014
Stem CellsInternational
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Enzyme Research
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
International Journal of
Microbiology
Journal of Marine Biology 5Ta
ble2Con
tinued
Perip
hytontaxa
Decem
ber
(Cellsm
Lminus1
)Janu
ary
(Cellsm
Lminus1
)February
(Cellsm
Lminus1
)March
(Cellsm
Lminus1
)Ap
ril(C
ellsm
Lminus1
)May
(Cellsm
Lminus1
)Au
lacoseira
islandica
subspHelv
etica
OM
ull
9840
134
192
271
285
Aulacoseira
granulata(Ehr)
189
115
337
414
541
702
Aulacoseira
italica(Ehr)
1333
103
175
203
198
Hem
idiscus
cuneiform
is29
3521
Cyclo
tella
meneghinianaKu
tzexBr Oslash
7218
108
67Co
cconeis
pediculusE
hr
4862
4898
72Rh
izosolenialongise
ta12
11Rh
izosoleniahebetata
Bail
14Order
IIPennales
Eunotia
arcusE
hr
7237
2737
Diatomatenu
isBo
ry117
121
113
67Cy
mbella
ventric
osaAgardh
3121
2427
34SurirelladebesiTu
rpin
2427
Surirellarobu
stavarsplen
dida
21Surirellarobu
stavararmata
17Surirellalin
earis
Turpin
1947
3827
31Synedraacus
Ehr
2131
Synedraulna
varcontractaEh
r22
1821
38Staurosirellalep
tosta
uron
14Asterio
nella
form
osaHassall
21207
Gyrosig
mascalproidesH
assall
19Gy
rosig
maattenu
atum
Hassall
1613
Gom
phonem
aparvulum
Ehr
2117
2436
31Na
viculalanceolata
Bory
98Na
viculapupu
laKu
tzvarrectangularisGrun
Com
pr
32Na
vicularadiosa
1928
52Na
viculamargalithii
2357
3837
Stauroneisanceps
27Nitzschiaacic
ularisKu
tz
5237
33Nitzschiadissipata
1828
27Nitzschiainterm
edia
3131
3454
4241
Nitzschiainconspicua
3132
3851
Nitzschiaclo
steriu
m31
32Nitzschiagracilis
3129
44Pinn
ulariaacrosphaeria(Breb)v
arm
inor
Kutz
2736
Pinn
ulariagibba
1731
Pseudosta
urosira
brevistria
ta11
AmphoraovalisKu
tz
4752
Epith
emiaargusv
arlongicornisGrun
3919
Epith
emiasorex
47Rh
opalodiaoperculata
(Ehr)Muller
21Ac
hnanthidium
lanceolatum
Kutz
2116
Achn
anthidium
linearis
Kutz
1227
6 Journal of Marine Biology
Table2Con
tinued
Perip
hytontaxa
Decem
ber
(Cellsm
Lminus1
)Janu
ary
(Cellsm
Lminus1
)February
(Cellsm
Lminus1
)March
(Cellsm
Lminus1
)Ap
ril(C
ellsm
Lminus1
)May
(Cellsm
Lminus1
)Ph
ylum
Chlorop
hyta
ClassCh
loroph
yceae
Order
ICh
lorococcales
Ankistrodesmus
falca
tusR
alfsvarmira
bilis
Westflongiseta
Nygaard
29An
kistrodesmus
falca
tusR
alfsvarspirilliform
isWest
32An
kistrodesmus
falca
tusR
alfs
18An
kistrodesmus
falca
tusR
alfsvarsetiformisNygaard
fbrevisNygaard
22An
kistrodesmus
gracilisC
orda
21An
kistrodesmus
braianus
24Scenedesmus
armatus
Chod
at19
2311
13Scenedesmus
perfo
ratesM
eyen
31Scenedesmus
dispar
fcanobe
2-cellu
laire
1114
1222
Scenedesmus
quadric
auda
1119
17Ac
tinastru
mHantzschiiL
agerheim
11Kirchn
eriellaspSchmidle
7Tetra
strum
stauroeniaeform
e16
Tetra
strum
heteracanthu
mfepinep
arcellu
le14
13Selen
astru
mgracile
Reinsch
13Pediastru
msim
plex
Meyen
17Pediastru
mdu
plex
Meyen
17Pediastru
mbiradiatum
varlongico
rnutum
16Pediastru
mtetra
sRalfs
1711
Qua
drigulaclo
sterio
ides
11Crucigeniatetra
pedia(K
irch)W
estetG
S
1417
Crucigeniaminim
aBrun
nthaler
1416
Order
IIZ
ygnematales
Spiro
gyra
spLink
37
Closteriu
mkutzingiifsigmoides
2226
Closteriu
mjen
neriRa
lfs21
Closteriu
mparvulum
Nag
32Staurastrum
pingue
Meyen
exRa
lfs19
18Stau
rastrum
cyclo
canthu
mvarub
acanthum
vuea
picale
2113
Staurodesm
usdickiei
varmaxim
us14
Cosm
arium
spC
orda
exRa
lfs13
Cosm
arium
scottii
18Co
smarium
trachypleu
rum
12Co
smarium
sinostegosv
arobstusiu
s7
Totalspecies
diversity
(119878)
2426
2363
4149
Totalspecies
abun
dance
1169
738
2009
3490
3363
3767
Journal of Marine Biology 7
(PO4-P le 078) silicate (SiO
3le 080) and sulphate (le130)
Periphyton chlorophyll 119886 reached a peak value (0003mgL)recorded in February and April while its lower value(0001mgL) was recorded in March with a mean value of00023mgL Biochemical oxygen demand reached a peakvalue (48mgL) recorded in December and the lowest value(04mgL) was recorded in January with a mean value of2317mgL Chemical oxygen demand value ranged between15mgL (December) and 37mgL (March) with amean valueof 231mgL Dissolved oxygen demand (DO) value reacheda peak value (10mgL) recorded in January and a lower value(45mgL) was recorded in February with a mean value of624mgL
The checklist of the periphyton species between Decem-ber 2012 and May 2013 is presented in Table 2 A total of14 536 individuals of 104 species were recorded throughoutthe study period The total number of taxa varied from 24in December to 26 in January 23 in February 63 in March41 in April and 49 in May Diatom populations during bothseasonswere dominated by 10 centric diatoms and 34 pennatediatoms and a total of 19 species were recorded for Cyanobac-teria Five divisions were recorded with their percent-age of occurrence Bacillariophyta (8269) Cyanobacteria(1043) Chlorophyta (563) and Euglenophyta (115)The total amount of periphyton abundance shows a strongpositive correlation with water temperature (119903 = 0744) pH(119903 = 0797) rainfall (119903 = 0745) and sulphate (119903 = 0707)It also strongly correlates significantly with TDS (119903 = 0836lowast119875 gt 005) and with transparency (119903 = minus0886lowast 119875 gt 005)There was greater species richness during wet months thandry months with a value 119889 le 76 Shannon-Wiener diversityindex value was observed to be119867
119904le 147 (Table 4)
4 Discussion
The range value of the surface water temperature reported isnotable for tropics The highest water temperature observedin May could be a result of time of collection and heatcapacity of waterThe positive correlation that exists betweenrainfall and surface water temperature could explain thepossible effect of precipitation on temperature Nwankwo[28] reported that there are two main seasons in Nigeria dryseason (NovemberndashApril) and wet season (MayndashOctober)The rainy season is ecologically more important in coastalwaters and is bimodal in distribution Floods caused by rain-fall enrich the coastal environmental gradients (horizontaland vertical) With this seasonal pattern it was observedthat transparency total dissolved solids and total suspendedsolids increased with the onset of rainfallThemicronutrientsconcentration level increased as precipitation rate increasedprobably due to input from settlements and wetlands
Odum [29] related pH levels to the amount of carbonatepresent in the water and often considered it an indicator ofthe aquatic chemical environment The observed pH value(pH le 66) falls within the range reported by Nwankwo andAkinsoji [30] for Epe Lagoon The pH value could mainlybe controlled by freshwater swamp exudates that regulate theacidity of the water body Change in pH value has a profound
Table 3 Pearson correlation coefficient matrix of water qualityindices total periphyton abundance and rainfall from December2012 to May 2013 at Ejirin part of Epe Lagoon
ParametersTotal abundance Rainfall
Rainfall 0745 1Water temperature 0744 0855lowast
Transparency minus0886lowast minus0755pH 0797 065Conductivity 0115 0701TSS minus0423 minus0652TDS 0836lowast 0678Salinity 0403 minus0183Reactive nitrate minus0533 minus0375Reactive phosphate 0247 minus0319Sulphate 0707 0374Silicate minus0870lowast minus053Peri chlorophyll a minus0566 minus0007BOD minus0039 minus0398COD 0955lowastlowast 0587DO minus0597 minus0206lowastCorrelation is significant at 005 level (2-tailed)lowastlowastCorrelation is significant at 001 level (2-tailed)
effect on the conductivity level of the water Furthermore thehigh value of dissolved oxygen observed in January could be aresult of combined photosynthetic activity of themicroscopicplants whereas the low value may be attributed to bacterialdegradation of organic matter which was observed at theonset of precipitation
Hynes [31] reported that BOD values of 1-2mgL orless represent clean water of 4ndash7mgL represent slightlypolluted water and of more than 8mgL represent severepollution Therefore based on the above criteria the site wasrelatively clean except for December and March where levelsof contamination were reported The Shannon-Wiener indexof diversity of 1ndash3 according toWilh and Dorris [32] signifiesmoderately polluted water and above 3 signifies clean watersituation In this regard Shannon-Weiner index in Decemberand March in periphyton community may point towardsmoderate pollution at this period
However the chlorophyll 119886 for periphyton communityshowed a rhythmic patternwith nutrient levelmostly reactivenitrate This may explain the importance of reactive nitrateto periphyton community The periphyton abundance in thewet months differs significantly with that of dry months(119905lowast = 8799 119875 gt 005) This could be a result of favourableconditions during this time that resulted in themultiplicationof algal cell and additional input of pennate forms by thefloodsThe algal spectrum observed shows that diatoms werethe dominant species in periphyton community
Bowker and Denny [33] reported the limited growth ofattached diatoms in the dry season and the rapid growth ofmacrophyte tissue This may explain why more species wereobserved on macrophyte tissues in the wet months Some ofthe algae that were common members of the plankton but
8 Journal of Marine Biology
Table 4 Biological indices parameters at Ejirin part of Epe Lagoon from December 2012 to May 2013
Periphyton taxa December January February March April MayTotal species diversity (119878) 24 26 23 63 41 49Total abundance (119873) cellsmLminus1 1169 738 2009 3490 3363 3767Shannon-Wiener index (119867
119904) 117 128 115 147 126 127
Margalef rsquos index (119889) 326 379 289 76 493 583
were found in periphyton community were often trapped bythe roots of the plant like the centric diatoms However thecentric diatoms found in the periphyton community weretransit visitor caught up by the mesh formed of the waterhyacinth roots
The observations that diatoms dominate the periphytoncommunity onwater hyacinth confirm earlier reports [34 35]that diatomsweremore abundant in the algal spectrum of theLagos Lagoon complex
Round [36] observed the abundance of Eunotia sp onLemna roots whereas Bowker and Denny [33] reported thedominance of Achnanthes and Cocconeis sp on the rootsand leaves of Lemna respectively Cocconeis pediculus Ehrand Achnanthidium sp were only found in the periphytoncommunity with Cocconeis occurring all through the monthssuggesting a strong coexistence Cocconeis pediculus Ehroccurred in a range of conditions from clean to moderatelyenriched to much enriched waters Its presence and others(euglenoids blue green algae Nitzschia palea Surirella spPinnularia sp Gomphonema parvulum Mougeotia sp Spir-ogyra sp Trachelomonas affinis (Lemm) T ensifera DadayT gibberosa Playf Phormidium articulatum Lyngbya inter-media Cymbella ventricosa Eunotia arcus Surirella linearisAsterionella formosa Hassall N acicularis Amphora ovalisKutzAnkistrodesmus falcatus Scenedesmus armatusChodatand Closterium parvulum Nag) may suggest pollution byorganic materials
The abundance of periphyton species on the waterhyacinthmay be given a second thought to enhance the aqua-culture production in the area A high species level for bluegreen algae and euglenoids in the periphyton communitymay reveal its suitability in monitoring environmental stressin coastal waters
Conflict of Interests
The authors declare that there is no conflict of interestsregarding the publication of this paper
Acknowledgments
Special thanks are due to the staff of Marine Biology Labo-ratory University of Lagos and Professor D I Nwankwo forthe help throughout the study period
References
[1] H Schlorin ldquoThe water hyacinthmdasha sensitive indicator for theenvironmental status of certain tropical water SCOPEUNEPrdquoSonderband vol 58 pp 217ndash224 1985
[2] A B N Egborge ldquoWater hyacinthmdashbiological museumrdquo inProceedings of the International Workshop on Water Hyacinthpp 52ndash70 Lagos Nigeria August 1988
[3] J W Feminella and C P Hawkins ldquoInteractions betweenstream herbivores and periphyton a quantitative analysis ofpast experimentsrdquo Journal of the North American BenthologicalSociety vol 14 no 4 pp 465ndash509 1995
[4] G E HutchinsonATreatise on Limnology vol 3 of LimnologicaBotany John Wiley amp Sons New York NY USA 1975
[5] J Kalff Limnology Prentice Hall Upper Saddle River NJ USA2002
[6] A L Behning ldquoZur Erforschung der am Flussboden derWolgalebenden OrganismenrdquoMonographien der Biologischen Wolga-Station vol 1 no 1 p 398 1924
[7] W M B Cooke ldquoColonisation of artificial bare areas bymicroorganismsrdquo The Botanical Review vol 22 no 9 pp 613ndash638 1956
[8] R G Wetzel ldquoAttached algal-substrata interactions fact ormyth and when and howrdquo in Periphyton of Freshwater Ecosys-tems R G Wetzel Ed pp 207ndash215 W Junk Publishers TheHague The Netherlands 1983
[9] Y Vadeboncoeur D M Lodge and S R Carpenter ldquoWhole-lake fertilization effects on distribution of primary productionbetween benthic and pelagic habitatsrdquo Ecology vol 82 no 4 pp1065ndash1077 2001
[10] L Liboriussen andE Jeppesen ldquoTemporal dynamics in epipelicpelagic and epiphytic algal production in a clear and a turbidshallow lakerdquo Freshwater Biology vol 48 no 3 pp 418ndash4312003
[11] R E Hecky and R H Hesslein ldquoContributions of benthic algaeto lake food webs as revealed by stable isotope analysisrdquo Journalof the North American Benthological Society vol 14 no 4 pp631ndash653 1995
[12] R G Wetzel ldquoMicrocommunities and microgradients linkingnutrient regenerationmicrobialmutualism and high sustainedaquatic primary productionrdquo Netherlands Journal of AquaticEcology vol 27 no 1 pp 3ndash9 1993
[13] M J Vander Zanden and Y Vadeboncoeur ldquoFishes as integra-tors of benthic and pelagic food webs in lakesrdquo Ecology vol 83no 8 pp 2152ndash2161 2002
[14] D I Nwankwo and A Akinsoji ldquoPeriphyton algae of aeutrophic creek and their possible use as indicatorrdquo NigeriaJournal of Botany vol 1 pp 47ndash54 1998
[15] D I Nwankwo and A O Onitiri ldquoPeriphyton community onsubmerged aquatic macrophytes (horn wort and bladderwort)in Epe Lagoon Nigeriardquo Journal of Agricultural Science andTechnology vol 2 no 2 pp 135ndash141 1992
[16] R L Lowe and Y Pan ldquoBenthic algal communities as biologicalmonitorsrdquo in Algal Ecology Freshwater Benthic Ecosystems RJ Stevenson M L Bothwell and R L Lowe Eds p 753Academic Press San Diego Calif USA 1996
Journal of Marine Biology 9
[17] P V McCormick and R J Stevenson ldquoPeriphyton as a toolfor ecological assessment and management in the FloridaEvergladesrdquo Journal of Phycology vol 34 no 5 pp 726ndash7331998
[18] E E Gaiser D L Childers R D Jones J H Richards L JScinto and J C Trexler ldquoPeriphyton responses to eutrophica-tion in the Florida Everglades cross-system patterns of struc-tural and compositional changerdquo Limnology amp Oceanographyvol 51 no 1 pp 617ndash630 2006
[19] P SWelch LimnologicalMethodsMcGraw-Hill NewYorkNYUSA 1948
[20] APHA Standard Methods for the Examination of Water WasteWater American Public and Health Association AmericanWater Works Association and Water Environment Federation(WEF) 20th edition 1998
[21] J W Foerster and H E Schlichting Jr ldquoPhyco-periphyton in anoligotrophic lakerdquo Transactions of the American MicroscopicalSociety vol 84 no 4 pp 485ndash502 1965
[22] J B Lackey ldquoThe manipulation and counting of river planktonand changes in some organisms due to formalin preservationrdquoUS Public Health Reports vol 53 no 47 pp 2080ndash2093 1938
[23] G M Smith The Fresh-Water Algae of the United StatesMcGraw-Hill London UK 1950
[24] S L VanlandinghamGuide to Identification and EnvironmentalRequirements and Pollution Tolerance of Freshwater Blue-GreenAlgae (Cyanophyta) US Environmental Protection Agency(EPA) 1982
[25] L A Whitford and G H Schmacher A Manual of FreshwaterAlgae Sparks Press Raeigh NC USA 1973
[26] B J F Biggs and C Kilroy Stream Periphyton MonitoringManual NIWA Christchurch New Zealand 2000
[27] A E Ogbeidu Biostatistics A Practical Approach to Researchand Data Handling Mindex Publishing Company LimitedBenin City Nigeria 2005
[28] D I Nwankwo The Microalgae Our Indispensable Allies inAquatic Montoring and Biodiversity Sustainability InauguralLecture Series University of Lagos Press 2004
[29] H T Odum ldquoTrophic structure and productivity of SilverSprings Floridardquo Ecological Monographs vol 27 pp 55ndash1121959
[30] D I Nwankwo andA Akinsoji ldquoEpiphyte community on waterhyacinth Eichhornia crassipes (MART SLOM) in coastal watersof southwestern Nigeriardquo Archiv fur Hydrobiologie vol 124 no4 pp 501ndash511 1992
[31] H B N Hynes The Biology of Polluted Waters LiverpoolUnibersity Press Liverpool UK 1960
[32] J Wilh and T C Dorris ldquoBiological parameters of waterqualityrdquo Bioscience vol 18 pp 477ndash481 1968
[33] D W Bowker and P Denny ldquoThe seasonal succession anddistribution of epiphytic algae in the phyllosphere of Lemnaminor LrdquoArchiv fur Hydrobiologie vol 90 no 1 pp 39ndash55 1980
[34] D I Nwankwo Seasonal changes of phytoplankton of Lagoslagoon and the adjacent sea in relation to environmental factors[PhD thesis] University of Lagos Lagos Nigeria 1984
[35] D I Nwankwo ldquoPhytoplankton of a sewage disposal site inLagos Lagoon Nigeriardquo The Journal of Biological Sciences vol1 no 2 pp 89ndash96 1986
[36] F E RoundTheBiology of Algae Edward Arnold London UK1965
Submit your manuscripts athttpwwwhindawicom
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Anatomy Research International
PeptidesInternational Journal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporation httpwwwhindawicom
International Journal of
Volume 2014
Zoology
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Molecular Biology International
GenomicsInternational Journal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
The Scientific World JournalHindawi Publishing Corporation httpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
BioinformaticsAdvances in
Marine BiologyJournal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Signal TransductionJournal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
BioMed Research International
Evolutionary BiologyInternational Journal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Biochemistry Research International
ArchaeaHindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Genetics Research International
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Advances in
Virolog y
Hindawi Publishing Corporationhttpwwwhindawicom
Nucleic AcidsJournal of
Volume 2014
Stem CellsInternational
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Enzyme Research
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
International Journal of
Microbiology
6 Journal of Marine Biology
Table2Con
tinued
Perip
hytontaxa
Decem
ber
(Cellsm
Lminus1
)Janu
ary
(Cellsm
Lminus1
)February
(Cellsm
Lminus1
)March
(Cellsm
Lminus1
)Ap
ril(C
ellsm
Lminus1
)May
(Cellsm
Lminus1
)Ph
ylum
Chlorop
hyta
ClassCh
loroph
yceae
Order
ICh
lorococcales
Ankistrodesmus
falca
tusR
alfsvarmira
bilis
Westflongiseta
Nygaard
29An
kistrodesmus
falca
tusR
alfsvarspirilliform
isWest
32An
kistrodesmus
falca
tusR
alfs
18An
kistrodesmus
falca
tusR
alfsvarsetiformisNygaard
fbrevisNygaard
22An
kistrodesmus
gracilisC
orda
21An
kistrodesmus
braianus
24Scenedesmus
armatus
Chod
at19
2311
13Scenedesmus
perfo
ratesM
eyen
31Scenedesmus
dispar
fcanobe
2-cellu
laire
1114
1222
Scenedesmus
quadric
auda
1119
17Ac
tinastru
mHantzschiiL
agerheim
11Kirchn
eriellaspSchmidle
7Tetra
strum
stauroeniaeform
e16
Tetra
strum
heteracanthu
mfepinep
arcellu
le14
13Selen
astru
mgracile
Reinsch
13Pediastru
msim
plex
Meyen
17Pediastru
mdu
plex
Meyen
17Pediastru
mbiradiatum
varlongico
rnutum
16Pediastru
mtetra
sRalfs
1711
Qua
drigulaclo
sterio
ides
11Crucigeniatetra
pedia(K
irch)W
estetG
S
1417
Crucigeniaminim
aBrun
nthaler
1416
Order
IIZ
ygnematales
Spiro
gyra
spLink
37
Closteriu
mkutzingiifsigmoides
2226
Closteriu
mjen
neriRa
lfs21
Closteriu
mparvulum
Nag
32Staurastrum
pingue
Meyen
exRa
lfs19
18Stau
rastrum
cyclo
canthu
mvarub
acanthum
vuea
picale
2113
Staurodesm
usdickiei
varmaxim
us14
Cosm
arium
spC
orda
exRa
lfs13
Cosm
arium
scottii
18Co
smarium
trachypleu
rum
12Co
smarium
sinostegosv
arobstusiu
s7
Totalspecies
diversity
(119878)
2426
2363
4149
Totalspecies
abun
dance
1169
738
2009
3490
3363
3767
Journal of Marine Biology 7
(PO4-P le 078) silicate (SiO
3le 080) and sulphate (le130)
Periphyton chlorophyll 119886 reached a peak value (0003mgL)recorded in February and April while its lower value(0001mgL) was recorded in March with a mean value of00023mgL Biochemical oxygen demand reached a peakvalue (48mgL) recorded in December and the lowest value(04mgL) was recorded in January with a mean value of2317mgL Chemical oxygen demand value ranged between15mgL (December) and 37mgL (March) with amean valueof 231mgL Dissolved oxygen demand (DO) value reacheda peak value (10mgL) recorded in January and a lower value(45mgL) was recorded in February with a mean value of624mgL
The checklist of the periphyton species between Decem-ber 2012 and May 2013 is presented in Table 2 A total of14 536 individuals of 104 species were recorded throughoutthe study period The total number of taxa varied from 24in December to 26 in January 23 in February 63 in March41 in April and 49 in May Diatom populations during bothseasonswere dominated by 10 centric diatoms and 34 pennatediatoms and a total of 19 species were recorded for Cyanobac-teria Five divisions were recorded with their percent-age of occurrence Bacillariophyta (8269) Cyanobacteria(1043) Chlorophyta (563) and Euglenophyta (115)The total amount of periphyton abundance shows a strongpositive correlation with water temperature (119903 = 0744) pH(119903 = 0797) rainfall (119903 = 0745) and sulphate (119903 = 0707)It also strongly correlates significantly with TDS (119903 = 0836lowast119875 gt 005) and with transparency (119903 = minus0886lowast 119875 gt 005)There was greater species richness during wet months thandry months with a value 119889 le 76 Shannon-Wiener diversityindex value was observed to be119867
119904le 147 (Table 4)
4 Discussion
The range value of the surface water temperature reported isnotable for tropics The highest water temperature observedin May could be a result of time of collection and heatcapacity of waterThe positive correlation that exists betweenrainfall and surface water temperature could explain thepossible effect of precipitation on temperature Nwankwo[28] reported that there are two main seasons in Nigeria dryseason (NovemberndashApril) and wet season (MayndashOctober)The rainy season is ecologically more important in coastalwaters and is bimodal in distribution Floods caused by rain-fall enrich the coastal environmental gradients (horizontaland vertical) With this seasonal pattern it was observedthat transparency total dissolved solids and total suspendedsolids increased with the onset of rainfallThemicronutrientsconcentration level increased as precipitation rate increasedprobably due to input from settlements and wetlands
Odum [29] related pH levels to the amount of carbonatepresent in the water and often considered it an indicator ofthe aquatic chemical environment The observed pH value(pH le 66) falls within the range reported by Nwankwo andAkinsoji [30] for Epe Lagoon The pH value could mainlybe controlled by freshwater swamp exudates that regulate theacidity of the water body Change in pH value has a profound
Table 3 Pearson correlation coefficient matrix of water qualityindices total periphyton abundance and rainfall from December2012 to May 2013 at Ejirin part of Epe Lagoon
ParametersTotal abundance Rainfall
Rainfall 0745 1Water temperature 0744 0855lowast
Transparency minus0886lowast minus0755pH 0797 065Conductivity 0115 0701TSS minus0423 minus0652TDS 0836lowast 0678Salinity 0403 minus0183Reactive nitrate minus0533 minus0375Reactive phosphate 0247 minus0319Sulphate 0707 0374Silicate minus0870lowast minus053Peri chlorophyll a minus0566 minus0007BOD minus0039 minus0398COD 0955lowastlowast 0587DO minus0597 minus0206lowastCorrelation is significant at 005 level (2-tailed)lowastlowastCorrelation is significant at 001 level (2-tailed)
effect on the conductivity level of the water Furthermore thehigh value of dissolved oxygen observed in January could be aresult of combined photosynthetic activity of themicroscopicplants whereas the low value may be attributed to bacterialdegradation of organic matter which was observed at theonset of precipitation
Hynes [31] reported that BOD values of 1-2mgL orless represent clean water of 4ndash7mgL represent slightlypolluted water and of more than 8mgL represent severepollution Therefore based on the above criteria the site wasrelatively clean except for December and March where levelsof contamination were reported The Shannon-Wiener indexof diversity of 1ndash3 according toWilh and Dorris [32] signifiesmoderately polluted water and above 3 signifies clean watersituation In this regard Shannon-Weiner index in Decemberand March in periphyton community may point towardsmoderate pollution at this period
However the chlorophyll 119886 for periphyton communityshowed a rhythmic patternwith nutrient levelmostly reactivenitrate This may explain the importance of reactive nitrateto periphyton community The periphyton abundance in thewet months differs significantly with that of dry months(119905lowast = 8799 119875 gt 005) This could be a result of favourableconditions during this time that resulted in themultiplicationof algal cell and additional input of pennate forms by thefloodsThe algal spectrum observed shows that diatoms werethe dominant species in periphyton community
Bowker and Denny [33] reported the limited growth ofattached diatoms in the dry season and the rapid growth ofmacrophyte tissue This may explain why more species wereobserved on macrophyte tissues in the wet months Some ofthe algae that were common members of the plankton but
8 Journal of Marine Biology
Table 4 Biological indices parameters at Ejirin part of Epe Lagoon from December 2012 to May 2013
Periphyton taxa December January February March April MayTotal species diversity (119878) 24 26 23 63 41 49Total abundance (119873) cellsmLminus1 1169 738 2009 3490 3363 3767Shannon-Wiener index (119867
119904) 117 128 115 147 126 127
Margalef rsquos index (119889) 326 379 289 76 493 583
were found in periphyton community were often trapped bythe roots of the plant like the centric diatoms However thecentric diatoms found in the periphyton community weretransit visitor caught up by the mesh formed of the waterhyacinth roots
The observations that diatoms dominate the periphytoncommunity onwater hyacinth confirm earlier reports [34 35]that diatomsweremore abundant in the algal spectrum of theLagos Lagoon complex
Round [36] observed the abundance of Eunotia sp onLemna roots whereas Bowker and Denny [33] reported thedominance of Achnanthes and Cocconeis sp on the rootsand leaves of Lemna respectively Cocconeis pediculus Ehrand Achnanthidium sp were only found in the periphytoncommunity with Cocconeis occurring all through the monthssuggesting a strong coexistence Cocconeis pediculus Ehroccurred in a range of conditions from clean to moderatelyenriched to much enriched waters Its presence and others(euglenoids blue green algae Nitzschia palea Surirella spPinnularia sp Gomphonema parvulum Mougeotia sp Spir-ogyra sp Trachelomonas affinis (Lemm) T ensifera DadayT gibberosa Playf Phormidium articulatum Lyngbya inter-media Cymbella ventricosa Eunotia arcus Surirella linearisAsterionella formosa Hassall N acicularis Amphora ovalisKutzAnkistrodesmus falcatus Scenedesmus armatusChodatand Closterium parvulum Nag) may suggest pollution byorganic materials
The abundance of periphyton species on the waterhyacinthmay be given a second thought to enhance the aqua-culture production in the area A high species level for bluegreen algae and euglenoids in the periphyton communitymay reveal its suitability in monitoring environmental stressin coastal waters
Conflict of Interests
The authors declare that there is no conflict of interestsregarding the publication of this paper
Acknowledgments
Special thanks are due to the staff of Marine Biology Labo-ratory University of Lagos and Professor D I Nwankwo forthe help throughout the study period
References
[1] H Schlorin ldquoThe water hyacinthmdasha sensitive indicator for theenvironmental status of certain tropical water SCOPEUNEPrdquoSonderband vol 58 pp 217ndash224 1985
[2] A B N Egborge ldquoWater hyacinthmdashbiological museumrdquo inProceedings of the International Workshop on Water Hyacinthpp 52ndash70 Lagos Nigeria August 1988
[3] J W Feminella and C P Hawkins ldquoInteractions betweenstream herbivores and periphyton a quantitative analysis ofpast experimentsrdquo Journal of the North American BenthologicalSociety vol 14 no 4 pp 465ndash509 1995
[4] G E HutchinsonATreatise on Limnology vol 3 of LimnologicaBotany John Wiley amp Sons New York NY USA 1975
[5] J Kalff Limnology Prentice Hall Upper Saddle River NJ USA2002
[6] A L Behning ldquoZur Erforschung der am Flussboden derWolgalebenden OrganismenrdquoMonographien der Biologischen Wolga-Station vol 1 no 1 p 398 1924
[7] W M B Cooke ldquoColonisation of artificial bare areas bymicroorganismsrdquo The Botanical Review vol 22 no 9 pp 613ndash638 1956
[8] R G Wetzel ldquoAttached algal-substrata interactions fact ormyth and when and howrdquo in Periphyton of Freshwater Ecosys-tems R G Wetzel Ed pp 207ndash215 W Junk Publishers TheHague The Netherlands 1983
[9] Y Vadeboncoeur D M Lodge and S R Carpenter ldquoWhole-lake fertilization effects on distribution of primary productionbetween benthic and pelagic habitatsrdquo Ecology vol 82 no 4 pp1065ndash1077 2001
[10] L Liboriussen andE Jeppesen ldquoTemporal dynamics in epipelicpelagic and epiphytic algal production in a clear and a turbidshallow lakerdquo Freshwater Biology vol 48 no 3 pp 418ndash4312003
[11] R E Hecky and R H Hesslein ldquoContributions of benthic algaeto lake food webs as revealed by stable isotope analysisrdquo Journalof the North American Benthological Society vol 14 no 4 pp631ndash653 1995
[12] R G Wetzel ldquoMicrocommunities and microgradients linkingnutrient regenerationmicrobialmutualism and high sustainedaquatic primary productionrdquo Netherlands Journal of AquaticEcology vol 27 no 1 pp 3ndash9 1993
[13] M J Vander Zanden and Y Vadeboncoeur ldquoFishes as integra-tors of benthic and pelagic food webs in lakesrdquo Ecology vol 83no 8 pp 2152ndash2161 2002
[14] D I Nwankwo and A Akinsoji ldquoPeriphyton algae of aeutrophic creek and their possible use as indicatorrdquo NigeriaJournal of Botany vol 1 pp 47ndash54 1998
[15] D I Nwankwo and A O Onitiri ldquoPeriphyton community onsubmerged aquatic macrophytes (horn wort and bladderwort)in Epe Lagoon Nigeriardquo Journal of Agricultural Science andTechnology vol 2 no 2 pp 135ndash141 1992
[16] R L Lowe and Y Pan ldquoBenthic algal communities as biologicalmonitorsrdquo in Algal Ecology Freshwater Benthic Ecosystems RJ Stevenson M L Bothwell and R L Lowe Eds p 753Academic Press San Diego Calif USA 1996
Journal of Marine Biology 9
[17] P V McCormick and R J Stevenson ldquoPeriphyton as a toolfor ecological assessment and management in the FloridaEvergladesrdquo Journal of Phycology vol 34 no 5 pp 726ndash7331998
[18] E E Gaiser D L Childers R D Jones J H Richards L JScinto and J C Trexler ldquoPeriphyton responses to eutrophica-tion in the Florida Everglades cross-system patterns of struc-tural and compositional changerdquo Limnology amp Oceanographyvol 51 no 1 pp 617ndash630 2006
[19] P SWelch LimnologicalMethodsMcGraw-Hill NewYorkNYUSA 1948
[20] APHA Standard Methods for the Examination of Water WasteWater American Public and Health Association AmericanWater Works Association and Water Environment Federation(WEF) 20th edition 1998
[21] J W Foerster and H E Schlichting Jr ldquoPhyco-periphyton in anoligotrophic lakerdquo Transactions of the American MicroscopicalSociety vol 84 no 4 pp 485ndash502 1965
[22] J B Lackey ldquoThe manipulation and counting of river planktonand changes in some organisms due to formalin preservationrdquoUS Public Health Reports vol 53 no 47 pp 2080ndash2093 1938
[23] G M Smith The Fresh-Water Algae of the United StatesMcGraw-Hill London UK 1950
[24] S L VanlandinghamGuide to Identification and EnvironmentalRequirements and Pollution Tolerance of Freshwater Blue-GreenAlgae (Cyanophyta) US Environmental Protection Agency(EPA) 1982
[25] L A Whitford and G H Schmacher A Manual of FreshwaterAlgae Sparks Press Raeigh NC USA 1973
[26] B J F Biggs and C Kilroy Stream Periphyton MonitoringManual NIWA Christchurch New Zealand 2000
[27] A E Ogbeidu Biostatistics A Practical Approach to Researchand Data Handling Mindex Publishing Company LimitedBenin City Nigeria 2005
[28] D I Nwankwo The Microalgae Our Indispensable Allies inAquatic Montoring and Biodiversity Sustainability InauguralLecture Series University of Lagos Press 2004
[29] H T Odum ldquoTrophic structure and productivity of SilverSprings Floridardquo Ecological Monographs vol 27 pp 55ndash1121959
[30] D I Nwankwo andA Akinsoji ldquoEpiphyte community on waterhyacinth Eichhornia crassipes (MART SLOM) in coastal watersof southwestern Nigeriardquo Archiv fur Hydrobiologie vol 124 no4 pp 501ndash511 1992
[31] H B N Hynes The Biology of Polluted Waters LiverpoolUnibersity Press Liverpool UK 1960
[32] J Wilh and T C Dorris ldquoBiological parameters of waterqualityrdquo Bioscience vol 18 pp 477ndash481 1968
[33] D W Bowker and P Denny ldquoThe seasonal succession anddistribution of epiphytic algae in the phyllosphere of Lemnaminor LrdquoArchiv fur Hydrobiologie vol 90 no 1 pp 39ndash55 1980
[34] D I Nwankwo Seasonal changes of phytoplankton of Lagoslagoon and the adjacent sea in relation to environmental factors[PhD thesis] University of Lagos Lagos Nigeria 1984
[35] D I Nwankwo ldquoPhytoplankton of a sewage disposal site inLagos Lagoon Nigeriardquo The Journal of Biological Sciences vol1 no 2 pp 89ndash96 1986
[36] F E RoundTheBiology of Algae Edward Arnold London UK1965
Submit your manuscripts athttpwwwhindawicom
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Anatomy Research International
PeptidesInternational Journal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporation httpwwwhindawicom
International Journal of
Volume 2014
Zoology
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Molecular Biology International
GenomicsInternational Journal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
The Scientific World JournalHindawi Publishing Corporation httpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
BioinformaticsAdvances in
Marine BiologyJournal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Signal TransductionJournal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
BioMed Research International
Evolutionary BiologyInternational Journal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Biochemistry Research International
ArchaeaHindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Genetics Research International
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Advances in
Virolog y
Hindawi Publishing Corporationhttpwwwhindawicom
Nucleic AcidsJournal of
Volume 2014
Stem CellsInternational
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Enzyme Research
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
International Journal of
Microbiology
Journal of Marine Biology 7
(PO4-P le 078) silicate (SiO
3le 080) and sulphate (le130)
Periphyton chlorophyll 119886 reached a peak value (0003mgL)recorded in February and April while its lower value(0001mgL) was recorded in March with a mean value of00023mgL Biochemical oxygen demand reached a peakvalue (48mgL) recorded in December and the lowest value(04mgL) was recorded in January with a mean value of2317mgL Chemical oxygen demand value ranged between15mgL (December) and 37mgL (March) with amean valueof 231mgL Dissolved oxygen demand (DO) value reacheda peak value (10mgL) recorded in January and a lower value(45mgL) was recorded in February with a mean value of624mgL
The checklist of the periphyton species between Decem-ber 2012 and May 2013 is presented in Table 2 A total of14 536 individuals of 104 species were recorded throughoutthe study period The total number of taxa varied from 24in December to 26 in January 23 in February 63 in March41 in April and 49 in May Diatom populations during bothseasonswere dominated by 10 centric diatoms and 34 pennatediatoms and a total of 19 species were recorded for Cyanobac-teria Five divisions were recorded with their percent-age of occurrence Bacillariophyta (8269) Cyanobacteria(1043) Chlorophyta (563) and Euglenophyta (115)The total amount of periphyton abundance shows a strongpositive correlation with water temperature (119903 = 0744) pH(119903 = 0797) rainfall (119903 = 0745) and sulphate (119903 = 0707)It also strongly correlates significantly with TDS (119903 = 0836lowast119875 gt 005) and with transparency (119903 = minus0886lowast 119875 gt 005)There was greater species richness during wet months thandry months with a value 119889 le 76 Shannon-Wiener diversityindex value was observed to be119867
119904le 147 (Table 4)
4 Discussion
The range value of the surface water temperature reported isnotable for tropics The highest water temperature observedin May could be a result of time of collection and heatcapacity of waterThe positive correlation that exists betweenrainfall and surface water temperature could explain thepossible effect of precipitation on temperature Nwankwo[28] reported that there are two main seasons in Nigeria dryseason (NovemberndashApril) and wet season (MayndashOctober)The rainy season is ecologically more important in coastalwaters and is bimodal in distribution Floods caused by rain-fall enrich the coastal environmental gradients (horizontaland vertical) With this seasonal pattern it was observedthat transparency total dissolved solids and total suspendedsolids increased with the onset of rainfallThemicronutrientsconcentration level increased as precipitation rate increasedprobably due to input from settlements and wetlands
Odum [29] related pH levels to the amount of carbonatepresent in the water and often considered it an indicator ofthe aquatic chemical environment The observed pH value(pH le 66) falls within the range reported by Nwankwo andAkinsoji [30] for Epe Lagoon The pH value could mainlybe controlled by freshwater swamp exudates that regulate theacidity of the water body Change in pH value has a profound
Table 3 Pearson correlation coefficient matrix of water qualityindices total periphyton abundance and rainfall from December2012 to May 2013 at Ejirin part of Epe Lagoon
ParametersTotal abundance Rainfall
Rainfall 0745 1Water temperature 0744 0855lowast
Transparency minus0886lowast minus0755pH 0797 065Conductivity 0115 0701TSS minus0423 minus0652TDS 0836lowast 0678Salinity 0403 minus0183Reactive nitrate minus0533 minus0375Reactive phosphate 0247 minus0319Sulphate 0707 0374Silicate minus0870lowast minus053Peri chlorophyll a minus0566 minus0007BOD minus0039 minus0398COD 0955lowastlowast 0587DO minus0597 minus0206lowastCorrelation is significant at 005 level (2-tailed)lowastlowastCorrelation is significant at 001 level (2-tailed)
effect on the conductivity level of the water Furthermore thehigh value of dissolved oxygen observed in January could be aresult of combined photosynthetic activity of themicroscopicplants whereas the low value may be attributed to bacterialdegradation of organic matter which was observed at theonset of precipitation
Hynes [31] reported that BOD values of 1-2mgL orless represent clean water of 4ndash7mgL represent slightlypolluted water and of more than 8mgL represent severepollution Therefore based on the above criteria the site wasrelatively clean except for December and March where levelsof contamination were reported The Shannon-Wiener indexof diversity of 1ndash3 according toWilh and Dorris [32] signifiesmoderately polluted water and above 3 signifies clean watersituation In this regard Shannon-Weiner index in Decemberand March in periphyton community may point towardsmoderate pollution at this period
However the chlorophyll 119886 for periphyton communityshowed a rhythmic patternwith nutrient levelmostly reactivenitrate This may explain the importance of reactive nitrateto periphyton community The periphyton abundance in thewet months differs significantly with that of dry months(119905lowast = 8799 119875 gt 005) This could be a result of favourableconditions during this time that resulted in themultiplicationof algal cell and additional input of pennate forms by thefloodsThe algal spectrum observed shows that diatoms werethe dominant species in periphyton community
Bowker and Denny [33] reported the limited growth ofattached diatoms in the dry season and the rapid growth ofmacrophyte tissue This may explain why more species wereobserved on macrophyte tissues in the wet months Some ofthe algae that were common members of the plankton but
8 Journal of Marine Biology
Table 4 Biological indices parameters at Ejirin part of Epe Lagoon from December 2012 to May 2013
Periphyton taxa December January February March April MayTotal species diversity (119878) 24 26 23 63 41 49Total abundance (119873) cellsmLminus1 1169 738 2009 3490 3363 3767Shannon-Wiener index (119867
119904) 117 128 115 147 126 127
Margalef rsquos index (119889) 326 379 289 76 493 583
were found in periphyton community were often trapped bythe roots of the plant like the centric diatoms However thecentric diatoms found in the periphyton community weretransit visitor caught up by the mesh formed of the waterhyacinth roots
The observations that diatoms dominate the periphytoncommunity onwater hyacinth confirm earlier reports [34 35]that diatomsweremore abundant in the algal spectrum of theLagos Lagoon complex
Round [36] observed the abundance of Eunotia sp onLemna roots whereas Bowker and Denny [33] reported thedominance of Achnanthes and Cocconeis sp on the rootsand leaves of Lemna respectively Cocconeis pediculus Ehrand Achnanthidium sp were only found in the periphytoncommunity with Cocconeis occurring all through the monthssuggesting a strong coexistence Cocconeis pediculus Ehroccurred in a range of conditions from clean to moderatelyenriched to much enriched waters Its presence and others(euglenoids blue green algae Nitzschia palea Surirella spPinnularia sp Gomphonema parvulum Mougeotia sp Spir-ogyra sp Trachelomonas affinis (Lemm) T ensifera DadayT gibberosa Playf Phormidium articulatum Lyngbya inter-media Cymbella ventricosa Eunotia arcus Surirella linearisAsterionella formosa Hassall N acicularis Amphora ovalisKutzAnkistrodesmus falcatus Scenedesmus armatusChodatand Closterium parvulum Nag) may suggest pollution byorganic materials
The abundance of periphyton species on the waterhyacinthmay be given a second thought to enhance the aqua-culture production in the area A high species level for bluegreen algae and euglenoids in the periphyton communitymay reveal its suitability in monitoring environmental stressin coastal waters
Conflict of Interests
The authors declare that there is no conflict of interestsregarding the publication of this paper
Acknowledgments
Special thanks are due to the staff of Marine Biology Labo-ratory University of Lagos and Professor D I Nwankwo forthe help throughout the study period
References
[1] H Schlorin ldquoThe water hyacinthmdasha sensitive indicator for theenvironmental status of certain tropical water SCOPEUNEPrdquoSonderband vol 58 pp 217ndash224 1985
[2] A B N Egborge ldquoWater hyacinthmdashbiological museumrdquo inProceedings of the International Workshop on Water Hyacinthpp 52ndash70 Lagos Nigeria August 1988
[3] J W Feminella and C P Hawkins ldquoInteractions betweenstream herbivores and periphyton a quantitative analysis ofpast experimentsrdquo Journal of the North American BenthologicalSociety vol 14 no 4 pp 465ndash509 1995
[4] G E HutchinsonATreatise on Limnology vol 3 of LimnologicaBotany John Wiley amp Sons New York NY USA 1975
[5] J Kalff Limnology Prentice Hall Upper Saddle River NJ USA2002
[6] A L Behning ldquoZur Erforschung der am Flussboden derWolgalebenden OrganismenrdquoMonographien der Biologischen Wolga-Station vol 1 no 1 p 398 1924
[7] W M B Cooke ldquoColonisation of artificial bare areas bymicroorganismsrdquo The Botanical Review vol 22 no 9 pp 613ndash638 1956
[8] R G Wetzel ldquoAttached algal-substrata interactions fact ormyth and when and howrdquo in Periphyton of Freshwater Ecosys-tems R G Wetzel Ed pp 207ndash215 W Junk Publishers TheHague The Netherlands 1983
[9] Y Vadeboncoeur D M Lodge and S R Carpenter ldquoWhole-lake fertilization effects on distribution of primary productionbetween benthic and pelagic habitatsrdquo Ecology vol 82 no 4 pp1065ndash1077 2001
[10] L Liboriussen andE Jeppesen ldquoTemporal dynamics in epipelicpelagic and epiphytic algal production in a clear and a turbidshallow lakerdquo Freshwater Biology vol 48 no 3 pp 418ndash4312003
[11] R E Hecky and R H Hesslein ldquoContributions of benthic algaeto lake food webs as revealed by stable isotope analysisrdquo Journalof the North American Benthological Society vol 14 no 4 pp631ndash653 1995
[12] R G Wetzel ldquoMicrocommunities and microgradients linkingnutrient regenerationmicrobialmutualism and high sustainedaquatic primary productionrdquo Netherlands Journal of AquaticEcology vol 27 no 1 pp 3ndash9 1993
[13] M J Vander Zanden and Y Vadeboncoeur ldquoFishes as integra-tors of benthic and pelagic food webs in lakesrdquo Ecology vol 83no 8 pp 2152ndash2161 2002
[14] D I Nwankwo and A Akinsoji ldquoPeriphyton algae of aeutrophic creek and their possible use as indicatorrdquo NigeriaJournal of Botany vol 1 pp 47ndash54 1998
[15] D I Nwankwo and A O Onitiri ldquoPeriphyton community onsubmerged aquatic macrophytes (horn wort and bladderwort)in Epe Lagoon Nigeriardquo Journal of Agricultural Science andTechnology vol 2 no 2 pp 135ndash141 1992
[16] R L Lowe and Y Pan ldquoBenthic algal communities as biologicalmonitorsrdquo in Algal Ecology Freshwater Benthic Ecosystems RJ Stevenson M L Bothwell and R L Lowe Eds p 753Academic Press San Diego Calif USA 1996
Journal of Marine Biology 9
[17] P V McCormick and R J Stevenson ldquoPeriphyton as a toolfor ecological assessment and management in the FloridaEvergladesrdquo Journal of Phycology vol 34 no 5 pp 726ndash7331998
[18] E E Gaiser D L Childers R D Jones J H Richards L JScinto and J C Trexler ldquoPeriphyton responses to eutrophica-tion in the Florida Everglades cross-system patterns of struc-tural and compositional changerdquo Limnology amp Oceanographyvol 51 no 1 pp 617ndash630 2006
[19] P SWelch LimnologicalMethodsMcGraw-Hill NewYorkNYUSA 1948
[20] APHA Standard Methods for the Examination of Water WasteWater American Public and Health Association AmericanWater Works Association and Water Environment Federation(WEF) 20th edition 1998
[21] J W Foerster and H E Schlichting Jr ldquoPhyco-periphyton in anoligotrophic lakerdquo Transactions of the American MicroscopicalSociety vol 84 no 4 pp 485ndash502 1965
[22] J B Lackey ldquoThe manipulation and counting of river planktonand changes in some organisms due to formalin preservationrdquoUS Public Health Reports vol 53 no 47 pp 2080ndash2093 1938
[23] G M Smith The Fresh-Water Algae of the United StatesMcGraw-Hill London UK 1950
[24] S L VanlandinghamGuide to Identification and EnvironmentalRequirements and Pollution Tolerance of Freshwater Blue-GreenAlgae (Cyanophyta) US Environmental Protection Agency(EPA) 1982
[25] L A Whitford and G H Schmacher A Manual of FreshwaterAlgae Sparks Press Raeigh NC USA 1973
[26] B J F Biggs and C Kilroy Stream Periphyton MonitoringManual NIWA Christchurch New Zealand 2000
[27] A E Ogbeidu Biostatistics A Practical Approach to Researchand Data Handling Mindex Publishing Company LimitedBenin City Nigeria 2005
[28] D I Nwankwo The Microalgae Our Indispensable Allies inAquatic Montoring and Biodiversity Sustainability InauguralLecture Series University of Lagos Press 2004
[29] H T Odum ldquoTrophic structure and productivity of SilverSprings Floridardquo Ecological Monographs vol 27 pp 55ndash1121959
[30] D I Nwankwo andA Akinsoji ldquoEpiphyte community on waterhyacinth Eichhornia crassipes (MART SLOM) in coastal watersof southwestern Nigeriardquo Archiv fur Hydrobiologie vol 124 no4 pp 501ndash511 1992
[31] H B N Hynes The Biology of Polluted Waters LiverpoolUnibersity Press Liverpool UK 1960
[32] J Wilh and T C Dorris ldquoBiological parameters of waterqualityrdquo Bioscience vol 18 pp 477ndash481 1968
[33] D W Bowker and P Denny ldquoThe seasonal succession anddistribution of epiphytic algae in the phyllosphere of Lemnaminor LrdquoArchiv fur Hydrobiologie vol 90 no 1 pp 39ndash55 1980
[34] D I Nwankwo Seasonal changes of phytoplankton of Lagoslagoon and the adjacent sea in relation to environmental factors[PhD thesis] University of Lagos Lagos Nigeria 1984
[35] D I Nwankwo ldquoPhytoplankton of a sewage disposal site inLagos Lagoon Nigeriardquo The Journal of Biological Sciences vol1 no 2 pp 89ndash96 1986
[36] F E RoundTheBiology of Algae Edward Arnold London UK1965
Submit your manuscripts athttpwwwhindawicom
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Anatomy Research International
PeptidesInternational Journal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporation httpwwwhindawicom
International Journal of
Volume 2014
Zoology
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Molecular Biology International
GenomicsInternational Journal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
The Scientific World JournalHindawi Publishing Corporation httpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
BioinformaticsAdvances in
Marine BiologyJournal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Signal TransductionJournal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
BioMed Research International
Evolutionary BiologyInternational Journal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Biochemistry Research International
ArchaeaHindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Genetics Research International
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Advances in
Virolog y
Hindawi Publishing Corporationhttpwwwhindawicom
Nucleic AcidsJournal of
Volume 2014
Stem CellsInternational
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Enzyme Research
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
International Journal of
Microbiology
8 Journal of Marine Biology
Table 4 Biological indices parameters at Ejirin part of Epe Lagoon from December 2012 to May 2013
Periphyton taxa December January February March April MayTotal species diversity (119878) 24 26 23 63 41 49Total abundance (119873) cellsmLminus1 1169 738 2009 3490 3363 3767Shannon-Wiener index (119867
119904) 117 128 115 147 126 127
Margalef rsquos index (119889) 326 379 289 76 493 583
were found in periphyton community were often trapped bythe roots of the plant like the centric diatoms However thecentric diatoms found in the periphyton community weretransit visitor caught up by the mesh formed of the waterhyacinth roots
The observations that diatoms dominate the periphytoncommunity onwater hyacinth confirm earlier reports [34 35]that diatomsweremore abundant in the algal spectrum of theLagos Lagoon complex
Round [36] observed the abundance of Eunotia sp onLemna roots whereas Bowker and Denny [33] reported thedominance of Achnanthes and Cocconeis sp on the rootsand leaves of Lemna respectively Cocconeis pediculus Ehrand Achnanthidium sp were only found in the periphytoncommunity with Cocconeis occurring all through the monthssuggesting a strong coexistence Cocconeis pediculus Ehroccurred in a range of conditions from clean to moderatelyenriched to much enriched waters Its presence and others(euglenoids blue green algae Nitzschia palea Surirella spPinnularia sp Gomphonema parvulum Mougeotia sp Spir-ogyra sp Trachelomonas affinis (Lemm) T ensifera DadayT gibberosa Playf Phormidium articulatum Lyngbya inter-media Cymbella ventricosa Eunotia arcus Surirella linearisAsterionella formosa Hassall N acicularis Amphora ovalisKutzAnkistrodesmus falcatus Scenedesmus armatusChodatand Closterium parvulum Nag) may suggest pollution byorganic materials
The abundance of periphyton species on the waterhyacinthmay be given a second thought to enhance the aqua-culture production in the area A high species level for bluegreen algae and euglenoids in the periphyton communitymay reveal its suitability in monitoring environmental stressin coastal waters
Conflict of Interests
The authors declare that there is no conflict of interestsregarding the publication of this paper
Acknowledgments
Special thanks are due to the staff of Marine Biology Labo-ratory University of Lagos and Professor D I Nwankwo forthe help throughout the study period
References
[1] H Schlorin ldquoThe water hyacinthmdasha sensitive indicator for theenvironmental status of certain tropical water SCOPEUNEPrdquoSonderband vol 58 pp 217ndash224 1985
[2] A B N Egborge ldquoWater hyacinthmdashbiological museumrdquo inProceedings of the International Workshop on Water Hyacinthpp 52ndash70 Lagos Nigeria August 1988
[3] J W Feminella and C P Hawkins ldquoInteractions betweenstream herbivores and periphyton a quantitative analysis ofpast experimentsrdquo Journal of the North American BenthologicalSociety vol 14 no 4 pp 465ndash509 1995
[4] G E HutchinsonATreatise on Limnology vol 3 of LimnologicaBotany John Wiley amp Sons New York NY USA 1975
[5] J Kalff Limnology Prentice Hall Upper Saddle River NJ USA2002
[6] A L Behning ldquoZur Erforschung der am Flussboden derWolgalebenden OrganismenrdquoMonographien der Biologischen Wolga-Station vol 1 no 1 p 398 1924
[7] W M B Cooke ldquoColonisation of artificial bare areas bymicroorganismsrdquo The Botanical Review vol 22 no 9 pp 613ndash638 1956
[8] R G Wetzel ldquoAttached algal-substrata interactions fact ormyth and when and howrdquo in Periphyton of Freshwater Ecosys-tems R G Wetzel Ed pp 207ndash215 W Junk Publishers TheHague The Netherlands 1983
[9] Y Vadeboncoeur D M Lodge and S R Carpenter ldquoWhole-lake fertilization effects on distribution of primary productionbetween benthic and pelagic habitatsrdquo Ecology vol 82 no 4 pp1065ndash1077 2001
[10] L Liboriussen andE Jeppesen ldquoTemporal dynamics in epipelicpelagic and epiphytic algal production in a clear and a turbidshallow lakerdquo Freshwater Biology vol 48 no 3 pp 418ndash4312003
[11] R E Hecky and R H Hesslein ldquoContributions of benthic algaeto lake food webs as revealed by stable isotope analysisrdquo Journalof the North American Benthological Society vol 14 no 4 pp631ndash653 1995
[12] R G Wetzel ldquoMicrocommunities and microgradients linkingnutrient regenerationmicrobialmutualism and high sustainedaquatic primary productionrdquo Netherlands Journal of AquaticEcology vol 27 no 1 pp 3ndash9 1993
[13] M J Vander Zanden and Y Vadeboncoeur ldquoFishes as integra-tors of benthic and pelagic food webs in lakesrdquo Ecology vol 83no 8 pp 2152ndash2161 2002
[14] D I Nwankwo and A Akinsoji ldquoPeriphyton algae of aeutrophic creek and their possible use as indicatorrdquo NigeriaJournal of Botany vol 1 pp 47ndash54 1998
[15] D I Nwankwo and A O Onitiri ldquoPeriphyton community onsubmerged aquatic macrophytes (horn wort and bladderwort)in Epe Lagoon Nigeriardquo Journal of Agricultural Science andTechnology vol 2 no 2 pp 135ndash141 1992
[16] R L Lowe and Y Pan ldquoBenthic algal communities as biologicalmonitorsrdquo in Algal Ecology Freshwater Benthic Ecosystems RJ Stevenson M L Bothwell and R L Lowe Eds p 753Academic Press San Diego Calif USA 1996
Journal of Marine Biology 9
[17] P V McCormick and R J Stevenson ldquoPeriphyton as a toolfor ecological assessment and management in the FloridaEvergladesrdquo Journal of Phycology vol 34 no 5 pp 726ndash7331998
[18] E E Gaiser D L Childers R D Jones J H Richards L JScinto and J C Trexler ldquoPeriphyton responses to eutrophica-tion in the Florida Everglades cross-system patterns of struc-tural and compositional changerdquo Limnology amp Oceanographyvol 51 no 1 pp 617ndash630 2006
[19] P SWelch LimnologicalMethodsMcGraw-Hill NewYorkNYUSA 1948
[20] APHA Standard Methods for the Examination of Water WasteWater American Public and Health Association AmericanWater Works Association and Water Environment Federation(WEF) 20th edition 1998
[21] J W Foerster and H E Schlichting Jr ldquoPhyco-periphyton in anoligotrophic lakerdquo Transactions of the American MicroscopicalSociety vol 84 no 4 pp 485ndash502 1965
[22] J B Lackey ldquoThe manipulation and counting of river planktonand changes in some organisms due to formalin preservationrdquoUS Public Health Reports vol 53 no 47 pp 2080ndash2093 1938
[23] G M Smith The Fresh-Water Algae of the United StatesMcGraw-Hill London UK 1950
[24] S L VanlandinghamGuide to Identification and EnvironmentalRequirements and Pollution Tolerance of Freshwater Blue-GreenAlgae (Cyanophyta) US Environmental Protection Agency(EPA) 1982
[25] L A Whitford and G H Schmacher A Manual of FreshwaterAlgae Sparks Press Raeigh NC USA 1973
[26] B J F Biggs and C Kilroy Stream Periphyton MonitoringManual NIWA Christchurch New Zealand 2000
[27] A E Ogbeidu Biostatistics A Practical Approach to Researchand Data Handling Mindex Publishing Company LimitedBenin City Nigeria 2005
[28] D I Nwankwo The Microalgae Our Indispensable Allies inAquatic Montoring and Biodiversity Sustainability InauguralLecture Series University of Lagos Press 2004
[29] H T Odum ldquoTrophic structure and productivity of SilverSprings Floridardquo Ecological Monographs vol 27 pp 55ndash1121959
[30] D I Nwankwo andA Akinsoji ldquoEpiphyte community on waterhyacinth Eichhornia crassipes (MART SLOM) in coastal watersof southwestern Nigeriardquo Archiv fur Hydrobiologie vol 124 no4 pp 501ndash511 1992
[31] H B N Hynes The Biology of Polluted Waters LiverpoolUnibersity Press Liverpool UK 1960
[32] J Wilh and T C Dorris ldquoBiological parameters of waterqualityrdquo Bioscience vol 18 pp 477ndash481 1968
[33] D W Bowker and P Denny ldquoThe seasonal succession anddistribution of epiphytic algae in the phyllosphere of Lemnaminor LrdquoArchiv fur Hydrobiologie vol 90 no 1 pp 39ndash55 1980
[34] D I Nwankwo Seasonal changes of phytoplankton of Lagoslagoon and the adjacent sea in relation to environmental factors[PhD thesis] University of Lagos Lagos Nigeria 1984
[35] D I Nwankwo ldquoPhytoplankton of a sewage disposal site inLagos Lagoon Nigeriardquo The Journal of Biological Sciences vol1 no 2 pp 89ndash96 1986
[36] F E RoundTheBiology of Algae Edward Arnold London UK1965
Submit your manuscripts athttpwwwhindawicom
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Anatomy Research International
PeptidesInternational Journal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporation httpwwwhindawicom
International Journal of
Volume 2014
Zoology
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Molecular Biology International
GenomicsInternational Journal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
The Scientific World JournalHindawi Publishing Corporation httpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
BioinformaticsAdvances in
Marine BiologyJournal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Signal TransductionJournal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
BioMed Research International
Evolutionary BiologyInternational Journal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Biochemistry Research International
ArchaeaHindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Genetics Research International
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Advances in
Virolog y
Hindawi Publishing Corporationhttpwwwhindawicom
Nucleic AcidsJournal of
Volume 2014
Stem CellsInternational
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Enzyme Research
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
International Journal of
Microbiology
Journal of Marine Biology 9
[17] P V McCormick and R J Stevenson ldquoPeriphyton as a toolfor ecological assessment and management in the FloridaEvergladesrdquo Journal of Phycology vol 34 no 5 pp 726ndash7331998
[18] E E Gaiser D L Childers R D Jones J H Richards L JScinto and J C Trexler ldquoPeriphyton responses to eutrophica-tion in the Florida Everglades cross-system patterns of struc-tural and compositional changerdquo Limnology amp Oceanographyvol 51 no 1 pp 617ndash630 2006
[19] P SWelch LimnologicalMethodsMcGraw-Hill NewYorkNYUSA 1948
[20] APHA Standard Methods for the Examination of Water WasteWater American Public and Health Association AmericanWater Works Association and Water Environment Federation(WEF) 20th edition 1998
[21] J W Foerster and H E Schlichting Jr ldquoPhyco-periphyton in anoligotrophic lakerdquo Transactions of the American MicroscopicalSociety vol 84 no 4 pp 485ndash502 1965
[22] J B Lackey ldquoThe manipulation and counting of river planktonand changes in some organisms due to formalin preservationrdquoUS Public Health Reports vol 53 no 47 pp 2080ndash2093 1938
[23] G M Smith The Fresh-Water Algae of the United StatesMcGraw-Hill London UK 1950
[24] S L VanlandinghamGuide to Identification and EnvironmentalRequirements and Pollution Tolerance of Freshwater Blue-GreenAlgae (Cyanophyta) US Environmental Protection Agency(EPA) 1982
[25] L A Whitford and G H Schmacher A Manual of FreshwaterAlgae Sparks Press Raeigh NC USA 1973
[26] B J F Biggs and C Kilroy Stream Periphyton MonitoringManual NIWA Christchurch New Zealand 2000
[27] A E Ogbeidu Biostatistics A Practical Approach to Researchand Data Handling Mindex Publishing Company LimitedBenin City Nigeria 2005
[28] D I Nwankwo The Microalgae Our Indispensable Allies inAquatic Montoring and Biodiversity Sustainability InauguralLecture Series University of Lagos Press 2004
[29] H T Odum ldquoTrophic structure and productivity of SilverSprings Floridardquo Ecological Monographs vol 27 pp 55ndash1121959
[30] D I Nwankwo andA Akinsoji ldquoEpiphyte community on waterhyacinth Eichhornia crassipes (MART SLOM) in coastal watersof southwestern Nigeriardquo Archiv fur Hydrobiologie vol 124 no4 pp 501ndash511 1992
[31] H B N Hynes The Biology of Polluted Waters LiverpoolUnibersity Press Liverpool UK 1960
[32] J Wilh and T C Dorris ldquoBiological parameters of waterqualityrdquo Bioscience vol 18 pp 477ndash481 1968
[33] D W Bowker and P Denny ldquoThe seasonal succession anddistribution of epiphytic algae in the phyllosphere of Lemnaminor LrdquoArchiv fur Hydrobiologie vol 90 no 1 pp 39ndash55 1980
[34] D I Nwankwo Seasonal changes of phytoplankton of Lagoslagoon and the adjacent sea in relation to environmental factors[PhD thesis] University of Lagos Lagos Nigeria 1984
[35] D I Nwankwo ldquoPhytoplankton of a sewage disposal site inLagos Lagoon Nigeriardquo The Journal of Biological Sciences vol1 no 2 pp 89ndash96 1986
[36] F E RoundTheBiology of Algae Edward Arnold London UK1965
Submit your manuscripts athttpwwwhindawicom
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Anatomy Research International
PeptidesInternational Journal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporation httpwwwhindawicom
International Journal of
Volume 2014
Zoology
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Molecular Biology International
GenomicsInternational Journal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
The Scientific World JournalHindawi Publishing Corporation httpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
BioinformaticsAdvances in
Marine BiologyJournal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Signal TransductionJournal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
BioMed Research International
Evolutionary BiologyInternational Journal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Biochemistry Research International
ArchaeaHindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Genetics Research International
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Advances in
Virolog y
Hindawi Publishing Corporationhttpwwwhindawicom
Nucleic AcidsJournal of
Volume 2014
Stem CellsInternational
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Enzyme Research
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
International Journal of
Microbiology
Submit your manuscripts athttpwwwhindawicom
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Anatomy Research International
PeptidesInternational Journal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporation httpwwwhindawicom
International Journal of
Volume 2014
Zoology
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Molecular Biology International
GenomicsInternational Journal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
The Scientific World JournalHindawi Publishing Corporation httpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
BioinformaticsAdvances in
Marine BiologyJournal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Signal TransductionJournal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
BioMed Research International
Evolutionary BiologyInternational Journal of
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Biochemistry Research International
ArchaeaHindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Genetics Research International
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Advances in
Virolog y
Hindawi Publishing Corporationhttpwwwhindawicom
Nucleic AcidsJournal of
Volume 2014
Stem CellsInternational
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
Enzyme Research
Hindawi Publishing Corporationhttpwwwhindawicom Volume 2014
International Journal of
Microbiology