Imperial Journal of Interdisciplinary Research (IJIR) Vol ... · ecosystem, located in the...
Transcript of Imperial Journal of Interdisciplinary Research (IJIR) Vol ... · ecosystem, located in the...
Imperial Journal of Interdisciplinary Research (IJIR)
Vol-2, Issue-12, 2016
ISSN: 2454-1362, http://www.onlinejournal.in
Imperial Journal of Interdisciplinary Research (IJIR) Page 2174
Wetland Water Level Analysis and Prediction:
A Case Study on Hakaluki Haor
Imranur Rahman1, Luthfur Rahman
2 & Badhan Talukder
3
Abstract: Wetlands are considered as the world’s most productive ecosystems as they provide a wide
range of economic, societal and ecological
benefits. Hakaluki haor, which is the country's
largest inland freshwater wetland ecosystem owing
to its ecological significance. The water-level
regime of this wetland is regarded to be an
important factor for its ecosystem functioning that
affects differently. This paper mainly focused on
studying the past trend and employing the Time
series analysis in order to forecast which leads to
assess the ecological impact. Juri River, having
connection with Hakaluki haor is brought into
consideration to collect data as a secondary
source. The variation of the water level is found
stable during the time period of January to March
where the highest disparity noticed at the time
period of April to October. The study suggests that
more hydrometric stations should be incorporated
in order to secure an upgrade assessment of the
water level analysis.
1. Introduction
Wetlands are characterized by the areas under
water wholly or partially. It is considered as the
world’s most productive ecosystems as they protect
and improve water quality, provide fish and
wildlife habitats, store floodwaters and maintain
surface water flow during dry periods. Wetlands
are playing an enormous role in production of
ecosystems on the Earth [14], and it provides so
many services for human welfare [31]. Wetlands
hold a great importance in both ecology and inland
freshwater fisheries by supporting a wide range of
invertebrate fauna, providing feeding grounds for
young and growing fish and provide refugia against
predators [3,12]. According to Mitsch and
Gosselink, the wetlands are interfaces between
terrestrial and aquatic ecosystems [20] where the
floodplain is a broad term used to refer to one or
more wetland types [28].
The wetland of Bangladesh is significant in the
world and is home to the number of fish, plants,
birds and other fauna. In Bangladesh around four
million hectares of land are flooded each year
during the monsoon (rainy) season, and over a
large portion of the nation is submerged in an
unusual flood year [2]. It gives the natural
surroundings to more than 260 fish species [27]
and a huge number of moving flying birds [6], and
sustenance for a huge number of family units in
bucolic Bangladesh, especially poor people.
Upwards of 80% of provincial families capture fish
for sustenance or to sell [20,32,13] and around 60%
of creature protein utilization originates from fish
[4].
Haors are floodplain lake and marsh frameworks,
generally portrayed as "bowl-molded depression
among the common levees of a river, that are
overflowing each year by rainstorm surges from
April/May until October" [23]. Hakaluki haor is the
country's largest inland freshwater wetland
ecosystem, located in the Fenchuganj and
Golapganj upazila, sub-district of Sylhet district,
and also Baralekha, Juri and Kulaura upazila in the
Moulvibazar district. There are more than 238
small, medium and large interconnecting beels,
some of which are perennial and others seasonal.
The region is surrounded nearly 4,400 ha by beels
during dry season. Due to precipitation, almost
every part of the haor remains under water, which
exists up to half of the year. Rivers namely Juri,
sonai, Damini, Fanai and Kuiachara are the water
sources of this haor where Juri and Sonai have
originated from India. A range of wildlife and
aquatic resources once supported by the Hakaluki
haor. In any case, lately this has turned into a quick
debased terrain and confronting expanded weights
and dangers from various sources, including over
utilization of its resources by nearby individuals
[8].
The water stages in Hakaluki haor fluctuate
typically as a result of the difference between the
inflow and the outflow. The intensity of
precipitation, the morphological attributes of the
haor and its watershed as well as the temperature
and wind speed (which indicated the water
losses) is the elements immensely affect the
deviation of these magnitudes.
Periodically, at the end of the rainy season wetland
fluctuate by its upper limit where at the end of the
dry season it appears its lower limit. The wetlands
and shallow lakes are the focal points for
evaluating the WLF by a greater part of researchers
[18]. For the compelling survival and well-being of
many species, these natural fluctuations are an
intrinsic feature of haor ecosystems that demand
their biological clock to those variations and
Imperial Journal of Interdisciplinary Research (IJIR)
Vol-2, Issue-12, 2016
ISSN: 2454-1362, http://www.onlinejournal.in
Imperial Journal of Interdisciplinary Research (IJIR) Page 2175
requiring a variety of services for the ecological
community [14,35]. Despite that, extreme WLF has
negative impacts on the human and the ecosystems
[7].
A relatively broad study reveals that excessive as
well as diminishing WLF not only lessens the
ecosystem functioning, but eventually brings the
clean water into the turbid water (Coops et al.
2003, Beklioglu et al. 2007). The alternation of
water level can also be seen as the part of
environmental change and may lead to soil erosion
[30].The extent of fluctuation as well as the
temporal order of the minimum and maximum
water levels and the alternation rate of water level
impacted natural topography of the water level
regime [34]. The wetland formation, activity and
biodiversity are more prone to more critical
impacts by excessive WLF than the ongoing
climate change [1,16].The ecological sustainability
of wetland and rivers are threatened by the
changing flow regimes [19,22,29,36]. A wide range
of spatial and temporal scales of the watershed
ecology is impacted by the flowing water across
the landscape [17,24,25,29,33].
Given this background, the primary goal of this
paper is to recapitulate the current knowledge and
analyse and forecast the water level fluctuation of
Hakaluki haor.
2. Study Area Situated in the north-east of Bangladesh
latitudinally between 24o35’N and 24o45’N and
Longitudinally between 92o00E and 92
o08E,
Hakaluki Haor is a shallow basin settled between
the Patharia and Madhab slopes in the East and the
Bhatera mountains toward the West. Officially,
Hakaluki Haor falls under the administration of two
regions (Moulvibazar and Sylhet), five Upazilas
(Kulaura, Barlekha, Fenchugonj, Paschim Juri, and
Golapgonj), and eleven Unions (Bhatera,
Baramchal, Bhakshimail, Jaifarnagar, Barni,
Talimpur, Sujanagar, Paschim Juri, Gilachhara,
Uttar Bade Pasha, and Sarifganj). Hakaluki Haor is
comprised of more than 238 little, medium and big
interconnecting beels some of which are permanent
and others cyclic (CNRS report).
Figure 1. Hakaluki Haor
3. Methodology
To evaluate the water level oscillation of Hakaluki
hour, the regular and periodical water level data of
the Juri River collected from Bangladesh Water
Development Board (BWDB). The changeable Juri
river leads to impact the water level of Hakaluki
haor, as it is directly being connected and fed by
the Juri river. Raising or lowering river stages
contributes the high water level, which assists to
detect the water level of the Hakaluki haor.The
collected data were processed to make them an
error free and demonstrated in the form of
illustrations and analysed to evaluate the pattern of
deviation by time.
Imperial Journal of Interdisciplinary Research (IJIR)
Vol-2, Issue-12, 2016
ISSN: 2454-1362, http://www.onlinejournal.in
Imperial Journal of Interdisciplinary Research (IJIR) Page 2176
Time series method is employed to predict the
maximum and minimum water level. This process
involves seeing a pattern in the historical data and
then infer the pattern into the hereafter. The
forecast is based exclusively on past values of the
variable and/or on past forecast errors.Time series
can be disintegrated into three parts, namely Trend
(Tt), Seasonal (St) and Irregular component (It).
Additive model and the Multiplicative model are
the two models of decomposition of time series.
Here, Multiplicative model is used for prediction.
Yt = St x Tt x It
Where,
Yt - the data at period t,
St- the seasonal component at period t,
Tt- the trend-cycle component at period t,
It- the irregular component at period t.
Steps of Forecasting by Multiplicative Time Series
Model:
1. At first, separate the trend –cycle
components from seasonal-irregular
components. Then, calculate the M-period
centred moving averages CMAt.
CMA(M) t= Tt× Ct
2.Separation of seasonal components (St) from
irregular (error) (It) components.
St x It = Yt / CMA(M)t
Thus, leaving only St value by removing
irregularity.
3.Calculate Yt (SA), the seasonally adjusted series
(deseasonalize) which has only seasonal
component removed:
Yt (SA ) = Yt / St = Tt x It
4.Using a simple linear regression analysis by
plotting deseasonalize data as the Y variable
against the X as a time code variable (t). After,
achieving the co-efficient data, then, data trend
component for forecast is obtained by the following
formula:
Tt= Intercept+ Slope* Time code (For
each row)
5.Finally, the forecast is obtained by the following
formula:
Forecast= Seasonal Component (St)
*Trend Component (Tt)
4. Results and Discussions
4.1. Data Analysis
Data of pre-existing sources have been applied in
this case study recorded by the Bangladesh
Agricultural Development Corporation. The data
are evaluated between the year of 2007 and 2015
days. After the average water level fluctuation
(maximum and minimum) of every month is
demonstrated graphically on a yearly basis. It is
manifest that the highest water level lies in the
month as of May to October where the lowest
water level occurred within the month in the
middle of November and December.
Imperial Journal of Interdisciplinary Research (IJIR)
Vol-2, Issue-12, 2016
ISSN: 2454-1362, http://www.onlinejournal.in
Imperial Journal of Interdisciplinary Research (IJIR) Page 2177
Figures 2-10. Monthly Maximum and Minimum Water Level from 2007 to 2015
The monthly mean water level information in the
period of time between 2007 to 2015 is shown
below. Both the maximum and minimum average
water level show an almost similar trend. The
Imperial Journal of Interdisciplinary Research (IJIR)
Vol-2, Issue-12, 2016
ISSN: 2454-1362, http://www.onlinejournal.in
Imperial Journal of Interdisciplinary Research (IJIR) Page 2178
three main phases are easily identified in the
illustration. The initial stage what is from January
to March is the most stable period with steady
water level variation. The greatest water level
disparity is found amid April to October, which is
in the medial phase. The ultimate stage, which,
commencing from November shows the
declining course of water level and lasts up to
December. In short, August is overwhelmingly the
peak (11.80) period for water level and November
(7.64) is the month with the mean water level. The
highest and lowest water level was correspondingly
11.80 m and 7.64 m. There were a few surprising
changes took place in the period beginning April to
November due to year to year diversity.
Figure 11. Comparisons of Monthly Water Level from 2007 to 2015
4.2. Data Prediction
The prediction for minimum water level is
exhibited below. In a multiple linear regression
model, the part of the divergence in the dependent
variable accounted by the explanatory variables is
measured by the adjusted coefficient of
determination (AR2). Here, the adjusted R
2 is less
than the coefficient of determination (R2) which
considered to be a good fit to assess. As the value
of “Significance F” is lower (0.0180) than 0.05, then the forecast is statistically significant and
hence multiple regression model is broadly
satisfactory. The model is useful and true to
forecast as the “P-value” for coefficient is also below 0.05.
Figure 12. Illustration of Predicted Minimum Water Level of 2016
Imperial Journal of Interdisciplinary Research (IJIR)
Vol-2, Issue-12, 2016
ISSN: 2454-1362, http://www.onlinejournal.in
Imperial Journal of Interdisciplinary Research (IJIR) Page 2179
ANOVA
df SS MS F Significance F
Regression 1 2.090130641 2.090131 5.764278 0.01809725
Residual 106 38.43566288 0.362601
Total 107 40.52579352
Coefficients Standard Error t Stat P-value Lower 95% Upper 95% Lower 95.0% Upper 95.0%
Intercept 8.495044059 0.116695834 72.79646 2.48E-92 8.263683225 8.72640489 8.263683225 8.72640489
t 0.004462316 0.001858608 2.400891 0.018097 0.000777444 0.00814719 0.000777444 0.00814719
Table 1. ANOVA Table Result of Predicted Minimum Water Level
5. Conclusion
The present analysis unveils that surface water
level in Hakaluki hoar area changes throughout the
year as regards to time. The highest oscillation
resides in the month starting April to October and
then starts descending from Novemver. January to
March proves the most unwavering periods
concerning the water level. Further probe is
required to contemplate the tendencies of water
level by evaluating the river stage data as of other
rivers. Statistics for more hydrometric stations
within the watershed should be incorporated to
secure an upgrade assessment of the water level.
The linkage between climate and hydrologic trends
should be ascertained by additional works.
6. References
[1] Abrahams C. 2008. Climate change and lakeshore
conservation: a model and review of management
techniques. Hydrobiologia. 613:33-43.
[2] Ali, M.Y. 1997. Fish,Water and People. University
Press Ltd.,Dhaka.
[3] Balirwa, J.S (1998), lake Victoria wetlands and the
ecology of the Nile Tilapia Oreochromis niloticus
Linne. A.A. Balkema Publishers, Rotterdam, The
Netherlands,247 pp
[4] BBS (1999), statistical Yearbook of Bangladesh,
Bangladesh Bureau of Statistics, Statistics Division,
Ministry of Planning, Government of Bangladesh,
Dhaka.
[5] Beklioglu M, Romo S, Kagalou I, Quintana X,
Becares E. 2007. State of the art in the functioning
of shallow Mediterranean lakes: workshop
conclusions. Hydrobiologia 584:317-326.
[6] Bird Life International (2004), important Bird Areas
in Asia: key sites for conservation.BirdLife
International, Cambridge UK.
[7] Bond NR, Lake PS, Arthington AH. 2008. The
impacts of drought on freshwater ecosystems: an
Australian perspective. Hydrobiologia. 600:3-16.
[8] Choudhury, J.K. and Faisal, A.M (2005), plant
Resources of Haors and Floodplains; An Overview.
IUCN-The World Conservation Union. Bangladesh
Country office, Dhaka.
[9] CNRS(Centre for Natural Resource Study). 2002.
Bio-physical characteristics of Hakaluki Haor.
a.conservation.BirdLife International, Cambridge
UK.
[10] Coops H, Beklioglu M, Crisman TL. 2003. The role
of water-level fluctuations in shallow lake
ecosystems - workshop conclusions. Hydrobiologia.
506(1-3):23-27.
[11] CWBMP (Coastal Wetland Biodiversity
Management Project), 2005. Baseline Survey of
Hakaluki Haor. Department of Environment, Center
for Natural Resource Studies (2005) CWBMP, DoE,
CNRS, Dhaka, Bangladesh.
[12] Denny, P. (ed) (1985), the ecology and management
of African wetland vegetation. Geobotany 6. Dr. W.
Junk Publishers, Dordrecht, The Netherlands, 344
pp
[13] FAP (1995), potential impacts of flood control on
the biological diversity and nutritional vale of
subsistence fisheries in Bangladesh. Flood Action
Plan 16 Environmental Study, Flood Plan
Coordination Organisation, Ministry of Water 25
Resources, Dhaka. (Report prepared by Irrigation
Support Project for Asia and the Near East).
[14] Gasith A, Gafny S. 1990. Effects of water level
fluctuation on the structure and function of the
littoral zone. In: Tilzer MM, Serruya C, editors.
Large Lakes: Ecological Structure and Function.
Berlin (Germany): Springer-Verlag. p. 156-171.
[15] Ghermandi, A., van den Bergh, J.C.J.M., Brander,
L.M., Nunes, P.A.L.D., 2008. The Economic Value
of Wetland Conservation andCreation: A Meta-
Analysis. [Working Paper 79]. Fondazione Eni
Enrico Mattei, Milan, Italy.
Imperial Journal of Interdisciplinary Research (IJIR)
Vol-2, Issue-12, 2016
ISSN: 2454-1362, http://www.onlinejournal.in
Imperial Journal of Interdisciplinary Research (IJIR) Page 2180
[16] Hulme PE. 2005. Adapting to climate change: is
there scope for ecological management in the face
of a global threat? J Appl Ecol. 42(5):784-794.
[17] Junk, W.J., P.B. Bayley, and R.E. Sparks. 1989. The
flood-pulse concept in river-floodplain systems.
Pages 110-127 in D.P. Dodge (ed.) Proceedings of
the International Large River Symposium (LARS),
Canadian Journal of Fisheries and Aquatic
Sciences Special Publication 106.
[18] Leira M, Cantonati M. 2008. Effects of water-level
fluctuations on lakes: an annotated bibliography.
Hydrobiologia. 613:171-184.
[19] Lundqvist, J. 1998. Avert looming hydrocide.
Ambio 27:428-33.
[20] Minkin, S.F., Rahman, M.M., Halder, S (1997), fish
biodiversity, human nutrition and environmental
restoration in Bangladesh. In: Tsai, C., Ali, M.Y.
(Eds.), Openwater Fisheries of Bangladesh, The
University Press Limited, Dhaka, pp 183–198.
[21] Mitsch, W.J. and Gosselink, J.G (2000), Wetlands,
3rd edn. Wiley, New York Matthews E (2004)
Traditional management revisited: Contemporary
challenges of community-based marine resource
management in Palau. Proceedings of the Coastal
Zone Asia Pacific Conference, Brisbane, 5–9
September, 2004
[22] Naiman, R.J., J.J. Magnuson, D.M. McKnight, and
J.A. Stanford. 1995. The Freshwater Imperative: A
Research Agenda. Island Press, Washington, D.C.,
165pp.
[23] Nishat, A. Hussain, Z. Roy, M.K. and Karim, A
(1993), freshwater Wetlands in Bangladesh: Issues
and Approaches for Management. IUCN-The World
Conservation Union, Gland, Switzerland
[24] Poff, N.L., and J.V. Ward. 1990. Physical habitat
template of lotic systems: recovery in the context of
historical patterns of spatiotemporal heterogeneity.
Environmental Management 14:629-645.
[25] Poff, N.L., J.D. Allan, M.B. Bain, J.R. Karr, K.L.
Prestegaard, B.D. Richter, R.E. Sparks, and J.C.
Stromberg. 1997. The natural flow regime.
BioScience 47:769-784.
[26] Priestly, M.B. (Ed.) (2005). Mathematics
Interdisciplinary Applications. Time Series
Analysis. Journal Of Royal Meteorological Society,
87,1-12
[27] Rahman, A.K.A (1989), freshwater Fish of
Bangladesh. Dhaka University, Dhaka. Ryan PA
(1991) The success of the gobidae in tropical Pacific
insular streams. NZ J Zool 18:25–30
[28] Ramsar Classification System for Wetland Type
(1971), reprinted from the Strategic Framework and
guidelines for the future development of the List of
Wetlands of International Importance.
[29] Sparks, R.E. 1995. Need for ecosystem management
of large rivers and floodplains. BioScience 45:168-
182.
[30] Suri.S., Ahmed.F., Yahaya.S., Mokhtar.Z. and
Halim.M., (2014), Climate Change Impact on Water
Level in Peninsular Malaysia, Journal of Civil
Engineering Research 2014, 4(3A): 228-232.
[31] ten Brink, P., Badura, T., Farmer, A., Russi, D.,
2012. The Economics of Ecosystem and
Biodiversity for Water and Wetlands: ABriefing
Note. Institute for European Environmental Policy,
London.
[32] Thompson, P.M., Sultana, P., Islam, M.N., Kabir,
M.M., Hossain, M.M. and Kabir, M.S (1999 23–28
August), an assessment of co-management
arrangements developed by the Community Based
Fisheries Management Project in Bangladesh, Paper
Presented at the International Workshop on
Fisheries Co-management, Penang, Malaysia
[33] Vannote R.L., G.W. Minshall, K.W. Cummins, J.R.
Sedell, and C.E. Cushing. 1980. The river
continuum concept. Canadian Journal of Fisheries
and Aquatic Sciences, 37:130-137.
[34] Wantzen KM, Junk, WJ, Rothhaupt KO. 2008a. An
extension of floodpulse concept (FPC) for lakes.
Hydrobiologia. 613:151-170.
[35] Wantzen KM, Rothhaupt KO, Mortl M, Cantonati
M, Laszlo GT, Fischer P. 2008b. Ecological effects
of water-level fluctuations in lakes: an urgent issue.
Hydrobiologia. 613:1-4.
[36] Ward, J.V., K. Tockner, and F. Schiemer. 1999.
Biodiversity of floodplain ecosystems: ecotones and
connectivity. Regulated Rivers: Research and
Management 15:125-139.