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Earth Sciences: an International Journal (ESIJ), Vol 1 No 1
1
SPATIAL COVERAGE OF WATER HYACINTH
INFESTATION AROUND LAKE TANA, ETHIOPIA
Melaku Getachew Ayalew
Ethiopian Environment and Forest Research Institute
ABSTRACT
Water hyacinth, Eichhornia Crassipes, is an aquatic invasive species which is native to South America. It
profoundly affects the tropical and subtropical region of the world. In addition, it is recognized as one of
the worst weeds and most aggressive invasive species by the International Union for theConservation of
Nature (IUCN). In Africa, Zimbabwe is one of the first African countries which water hyacinth was
officially recorded. In Ethiopia, it announced in 1956 in Koka Lake and Awash river. Water hyacinth
infestation around the Lake Tana is aggravated from time to time. This study was conducted on five
woredas (such as Dera, Fogera, Libokemkem, Gondar Zuria and Dembia) which have a higher infestation
of water hyacinth coverage. There were about 5394 hectares of water hyacinth areal coverage of the whole
woredas at the cost of the Lake. From those woredas, Dembia was holding most areal coverage (2563
hectares) of water hyacinth infestation. To determine the areal extent of water hyacinth around the lake,
consecutive ground control truck points was calibrated.
INTRODUCTION
Water hyacinth, Eichhorniacrassipes, is a perennial, herbaceous, aquatic plant and is Native to
the Amazon Basin in South America. Water hyacinth has emerged as a major weed in more than
50 countries in the tropical and subtropical regions of the world with profuse and permanent
impacts (Patel, 2012; Téllez et al., 2008; Samuel and Netsanet, 2014).Originally from the
Amazon Basin, its entry into Africa, Asia, Australia, and North America was facilitated by human
activities (Dagno et al., 2012). Water hyacinth has been identified by the International Union for
Conservation of Nature (IUCN) as one of the 100 most aggressive invasive species (Téllez et al.,
2008) and recognized as one of the top 10 worst weeds in the world (Gichuki et al., 2012; Patel,
2012). It is characterized by rapid growth rates, extensive dispersal capabilities, large and rapid
reproductive output and broad environmental tolerance (Zhang et al., 2010).
In Africa, where water hyacinth is listed by law as a noxious weed in several countries, it is the
most widespread and damaging aquatic plant species. The first African countrywhich water
hyacinth weed was officially recorded in Zimbabwe in 1937. In Ethiopia, water hyacinth was
announced in 1956 in Koka Lake and Awash River (Samuel and Netsanet, 2014; UNEP, 2013). It
also prevailed in most of rift valley lakes, canals, reservoirs and irrigation water supply within
different manifestation magnitude (Firehun et al, 2014). Lake Tana is the one in which water
hyacinth infestation highly occurred.
The economic impacts of the weed in seven African countries have been estimated at between
US$20-50 million every year. Across Africa, costs may be as much as US$100 million annually
(UNEP, 2006). The success of this invasive alien species is largely due to its reproductive output.
Water hyacinth can flower throughout the year and releases more than 3000 seeds per year. The
seeds are long-lived, up to 20 years (UNEP, 2013).
Water hyacinth has anegative ecological impact on freshwater bodies, suppressing all other
species growing in the vicinity. Large water hyacinth mats negatively affecting microbes,
prevents the growth and abundance of phytoplankton, prevent the transfer of oxygen from theair
to water bodies (Gichuki et al., 2012, UNEP, 2013). When the plant dies and sinks to the bottom
Earth Sciences: an International Journal (ESIJ), Vol 1 No 1
2
the decomposing biomass depletes oxygen content in thewater body. Death and decay of water
hyacinth vegetation in large masses deteriorate water quality and the quantity of potable water
and increases treatment costs for drinking water (Patel, 2012, Mironga et al., 2011, Ndimele et al.,
2011).
GIS and remote sensing have played an immense role to map the distribution and areal extent of
invasive species. As a result, it uses as a decision support system toolfor decision makers.
Integrated GIS and remote sensing have been applied to map the distribution of several plant and
animal species, their ecosystems, landscapes, bio-climatic conditions and factors facilitating
invasion (Los et al., 2002).The study has used both GIS and Remote sensing integrity to
demonstrate the spatial extent of water hyacinth infestation on the Lake Tana. Therefore, this is
significant for researchers, environmentalists, botanists, and decision supporters as a baseline
information to perform further analysis and decision making.
MATERIALS AND METHODOLOGIES
Data sources
The main sources of data for this paper were Google earth image, ground control GPS points, and
Sentinel 1 high-resolutionLandsat image has used for analysis.
Methodologies
Lake Tana is found in 100
58’-120
47’ N latitude and 360
45’-380
14’ E longitude. The water
hyacinth is highly infested at the coast of Dera, Fogera, Libokemkem, Gondar Zuria and Gorgora
woredas. GPS points were calibrated from at the coast of the lake where the weed is found and
the water hyacinth infestation inside the lake using local boats. The coordinate points were put in
ArcMap and convert them into shapefiles. Those shapefiles were open in Google Earth and
digitize by following the path of GPS truck points to calculate the area of water hyacinth
infestation coverage for each woreda.Besides, United State Geological Survey (USGS) earth
explorer imagery sentinel 1data was used as an input to nominate the area coverage by overlaying
vector polygon with image data.
Result and Discussion
The arealextent and magnitude of water hyacinth in each district (Woredas) is different according
to the result (Table 1).
Woredas Name Area Coverage in Hectare
Dera 260
Fogera 755
Libokemkem 1038
Gondar Zuria 780
Dembia 2563
Table 1: Area coverage of each woreda.
Water hyacinth in Dembiaworeda is higher than the remaining woredas as shown in the table
above. Around the coast of this woreda, agricultural activities highly occur and the water hyacinth
is highly affecting the growth and product of farmers’ crops. Most of the time, water hyacinth
growth depends on the landscape situation of the area. Under the shelter of huge trees and areas
Earth Sciences: an International Journal (ESIJ), Vol 1 No 1
3
which have shallow depth on the coast of the lake, the growth and greenness of this invasive
species are higher than those areas which have deep in depth. Coastal areas which are rocky in
nature, around the lake, has aminimum coverage of water hyacinth is available. For instance,
Deraworeda around the Tana Kirkos monastery, some parts of this monastery is covered by rocks.
And the remaining part of the monastery is covered by huge trees which have large canopy cover.
Water hyacinth area coverage and its extent around those two different land cover parts of
themonastery are significantly higher around the coast of large canopy tree coverage than the
rocky one.
There were about 5396 hectares of water hyacinth coverage has found in all woredas. Dembia
woreda has covered 2563 hectares of water hyacinth and adversely affected by this invasive
species than other woredas. Whereas, Dera woreda has the least areal extent coverage of water
hyacinth than other woredas. The thinner parts of the following map (Figure 1) demonstrated that
the areal extent of water hyacinth in that woreda/place is minimum coverage of water hyacinth
infestation than the remainingandvice versa.The violet color which is overlayedon the Sentinel 1
Landsat image (Figure 2) depicts that, the water hyacinth infestation of an areal extent from coast
to inside part of the lake.
Figure 1. The total areal extent of water hyacinth around Lake Tana.
Earth Sciences: an International Journal (ESIJ), Vol 1 No 1
4
Figure 2. Overlaid Sentinel 1 Landsat image with shape file of water hyacinth infestation.
REFERENCES
[1] Firehun, Y., Struik, P.C., Lantinga, E.A. and Taye, T. (2014). Water Hyacinth in the Rift Valley
Water Bodies of Ethiopia: Its Distribution, Socioeconomic Importance, and Management, Ethiopia.
[2] Gichuki, J., Omondi, R., Boera, P., Tom Okorut, T., SaidMatano, A., Jembe, T. and Ofulla, A.,
(2012). Water Hyacinth Eichhorniacrassipes (Mart.) Solms-Laubach Dynamics and Succession in the
Nyanza Gulf of Lake Victoria (East Africa): Implications forWater Quality and Biodiversity
Conservation. TheScientific World Journal Volume 2012, Article ID 106429, 10 pages
doi:10.1100/2012/106429.
[3] Los, S. O., Tucker, C. J., Anyamba, A., Cherlet, M., Collatz, G. J., Giglio, L., hall, F. G., & Kendall,
J. A. (2002). Environmental modeling with GIS and RS. Taylor & Francis, London.
[4] Mironga, J., Mathooko, J. and Anywhere, S., (2011). The Effect of Water Hyacinth
(EichhorniaCrassipes) Infestation on Phytoplankton Productivity in Lake Naivasha and the Status of
Control. Journal of Environmental Science and Engineering 5(10) 1252 1261.
[5] Ndimele, P., Kumolu-Johnson, C. and Anetekhai, M. (2011). The invasive aquatic macrophyte, water
hyacinth {Eichhorniacrassipes (Mart.) Solm-Laubach: Pontedericeae}: problems and prospects. Res J
Environ Sci 5:509–520.
[6] Patel, S.,(2012). Threats, management and envisaged utilizations of aquatic weed Eichhorniacrassipes
an overview. Rev Environ Sci Biotechnol (2012) 11:249–259. DOI 10.1007/s11157-012-9289-4.
[7] Samuel, T., and Netsanet, A. (2014). Prevalence and Intensity of Water Hyacinth Infestation in the
Water Bodies of Rift Valley, Ethiopia.
Earth Sciences: an International Journal (ESIJ), Vol 1 No 1
5
[8] Tellez, T., Lopez, E., Granado, G., Perez, E., Lopez, R., and Guzman, J., (2008). The water hyacinth,
Eichhorniacrassipes an invasive plant in the Guadiana River Basin (Spain). Aquatic Invasions 3, 42-
53.
[9] UNEP, (2006). Africa Environment Outlook 2. Division of Early Warning and Assessment, United
Nations Environment Programme, Nairobi.
[10] UNEP, (2013). Global Environment Alert Service. Taking the pulse of the planet connecting science
with policy, United Nation Environment Programme.
[11] Zhang, Y., Zhang, D., Barrett, S., 2010. Genetic uniformity characterizes the invasive spread of water
hyacinth (Eichhorniacrassipes), a clonal aquatic plant. Molecular Ecology 19: 1774-1786.

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Spatial Coverage of Water Hyacinth Infestation Around Lake Tana, Ethiopia

  • 1. Earth Sciences: an International Journal (ESIJ), Vol 1 No 1 1 SPATIAL COVERAGE OF WATER HYACINTH INFESTATION AROUND LAKE TANA, ETHIOPIA Melaku Getachew Ayalew Ethiopian Environment and Forest Research Institute ABSTRACT Water hyacinth, Eichhornia Crassipes, is an aquatic invasive species which is native to South America. It profoundly affects the tropical and subtropical region of the world. In addition, it is recognized as one of the worst weeds and most aggressive invasive species by the International Union for theConservation of Nature (IUCN). In Africa, Zimbabwe is one of the first African countries which water hyacinth was officially recorded. In Ethiopia, it announced in 1956 in Koka Lake and Awash river. Water hyacinth infestation around the Lake Tana is aggravated from time to time. This study was conducted on five woredas (such as Dera, Fogera, Libokemkem, Gondar Zuria and Dembia) which have a higher infestation of water hyacinth coverage. There were about 5394 hectares of water hyacinth areal coverage of the whole woredas at the cost of the Lake. From those woredas, Dembia was holding most areal coverage (2563 hectares) of water hyacinth infestation. To determine the areal extent of water hyacinth around the lake, consecutive ground control truck points was calibrated. INTRODUCTION Water hyacinth, Eichhorniacrassipes, is a perennial, herbaceous, aquatic plant and is Native to the Amazon Basin in South America. Water hyacinth has emerged as a major weed in more than 50 countries in the tropical and subtropical regions of the world with profuse and permanent impacts (Patel, 2012; Téllez et al., 2008; Samuel and Netsanet, 2014).Originally from the Amazon Basin, its entry into Africa, Asia, Australia, and North America was facilitated by human activities (Dagno et al., 2012). Water hyacinth has been identified by the International Union for Conservation of Nature (IUCN) as one of the 100 most aggressive invasive species (Téllez et al., 2008) and recognized as one of the top 10 worst weeds in the world (Gichuki et al., 2012; Patel, 2012). It is characterized by rapid growth rates, extensive dispersal capabilities, large and rapid reproductive output and broad environmental tolerance (Zhang et al., 2010). In Africa, where water hyacinth is listed by law as a noxious weed in several countries, it is the most widespread and damaging aquatic plant species. The first African countrywhich water hyacinth weed was officially recorded in Zimbabwe in 1937. In Ethiopia, water hyacinth was announced in 1956 in Koka Lake and Awash River (Samuel and Netsanet, 2014; UNEP, 2013). It also prevailed in most of rift valley lakes, canals, reservoirs and irrigation water supply within different manifestation magnitude (Firehun et al, 2014). Lake Tana is the one in which water hyacinth infestation highly occurred. The economic impacts of the weed in seven African countries have been estimated at between US$20-50 million every year. Across Africa, costs may be as much as US$100 million annually (UNEP, 2006). The success of this invasive alien species is largely due to its reproductive output. Water hyacinth can flower throughout the year and releases more than 3000 seeds per year. The seeds are long-lived, up to 20 years (UNEP, 2013). Water hyacinth has anegative ecological impact on freshwater bodies, suppressing all other species growing in the vicinity. Large water hyacinth mats negatively affecting microbes, prevents the growth and abundance of phytoplankton, prevent the transfer of oxygen from theair to water bodies (Gichuki et al., 2012, UNEP, 2013). When the plant dies and sinks to the bottom
  • 2. Earth Sciences: an International Journal (ESIJ), Vol 1 No 1 2 the decomposing biomass depletes oxygen content in thewater body. Death and decay of water hyacinth vegetation in large masses deteriorate water quality and the quantity of potable water and increases treatment costs for drinking water (Patel, 2012, Mironga et al., 2011, Ndimele et al., 2011). GIS and remote sensing have played an immense role to map the distribution and areal extent of invasive species. As a result, it uses as a decision support system toolfor decision makers. Integrated GIS and remote sensing have been applied to map the distribution of several plant and animal species, their ecosystems, landscapes, bio-climatic conditions and factors facilitating invasion (Los et al., 2002).The study has used both GIS and Remote sensing integrity to demonstrate the spatial extent of water hyacinth infestation on the Lake Tana. Therefore, this is significant for researchers, environmentalists, botanists, and decision supporters as a baseline information to perform further analysis and decision making. MATERIALS AND METHODOLOGIES Data sources The main sources of data for this paper were Google earth image, ground control GPS points, and Sentinel 1 high-resolutionLandsat image has used for analysis. Methodologies Lake Tana is found in 100 58’-120 47’ N latitude and 360 45’-380 14’ E longitude. The water hyacinth is highly infested at the coast of Dera, Fogera, Libokemkem, Gondar Zuria and Gorgora woredas. GPS points were calibrated from at the coast of the lake where the weed is found and the water hyacinth infestation inside the lake using local boats. The coordinate points were put in ArcMap and convert them into shapefiles. Those shapefiles were open in Google Earth and digitize by following the path of GPS truck points to calculate the area of water hyacinth infestation coverage for each woreda.Besides, United State Geological Survey (USGS) earth explorer imagery sentinel 1data was used as an input to nominate the area coverage by overlaying vector polygon with image data. Result and Discussion The arealextent and magnitude of water hyacinth in each district (Woredas) is different according to the result (Table 1). Woredas Name Area Coverage in Hectare Dera 260 Fogera 755 Libokemkem 1038 Gondar Zuria 780 Dembia 2563 Table 1: Area coverage of each woreda. Water hyacinth in Dembiaworeda is higher than the remaining woredas as shown in the table above. Around the coast of this woreda, agricultural activities highly occur and the water hyacinth is highly affecting the growth and product of farmers’ crops. Most of the time, water hyacinth growth depends on the landscape situation of the area. Under the shelter of huge trees and areas
  • 3. Earth Sciences: an International Journal (ESIJ), Vol 1 No 1 3 which have shallow depth on the coast of the lake, the growth and greenness of this invasive species are higher than those areas which have deep in depth. Coastal areas which are rocky in nature, around the lake, has aminimum coverage of water hyacinth is available. For instance, Deraworeda around the Tana Kirkos monastery, some parts of this monastery is covered by rocks. And the remaining part of the monastery is covered by huge trees which have large canopy cover. Water hyacinth area coverage and its extent around those two different land cover parts of themonastery are significantly higher around the coast of large canopy tree coverage than the rocky one. There were about 5396 hectares of water hyacinth coverage has found in all woredas. Dembia woreda has covered 2563 hectares of water hyacinth and adversely affected by this invasive species than other woredas. Whereas, Dera woreda has the least areal extent coverage of water hyacinth than other woredas. The thinner parts of the following map (Figure 1) demonstrated that the areal extent of water hyacinth in that woreda/place is minimum coverage of water hyacinth infestation than the remainingandvice versa.The violet color which is overlayedon the Sentinel 1 Landsat image (Figure 2) depicts that, the water hyacinth infestation of an areal extent from coast to inside part of the lake. Figure 1. The total areal extent of water hyacinth around Lake Tana.
  • 4. Earth Sciences: an International Journal (ESIJ), Vol 1 No 1 4 Figure 2. Overlaid Sentinel 1 Landsat image with shape file of water hyacinth infestation. REFERENCES [1] Firehun, Y., Struik, P.C., Lantinga, E.A. and Taye, T. (2014). Water Hyacinth in the Rift Valley Water Bodies of Ethiopia: Its Distribution, Socioeconomic Importance, and Management, Ethiopia. [2] Gichuki, J., Omondi, R., Boera, P., Tom Okorut, T., SaidMatano, A., Jembe, T. and Ofulla, A., (2012). Water Hyacinth Eichhorniacrassipes (Mart.) Solms-Laubach Dynamics and Succession in the Nyanza Gulf of Lake Victoria (East Africa): Implications forWater Quality and Biodiversity Conservation. TheScientific World Journal Volume 2012, Article ID 106429, 10 pages doi:10.1100/2012/106429. [3] Los, S. O., Tucker, C. J., Anyamba, A., Cherlet, M., Collatz, G. J., Giglio, L., hall, F. G., & Kendall, J. A. (2002). Environmental modeling with GIS and RS. Taylor & Francis, London. [4] Mironga, J., Mathooko, J. and Anywhere, S., (2011). The Effect of Water Hyacinth (EichhorniaCrassipes) Infestation on Phytoplankton Productivity in Lake Naivasha and the Status of Control. Journal of Environmental Science and Engineering 5(10) 1252 1261. [5] Ndimele, P., Kumolu-Johnson, C. and Anetekhai, M. (2011). The invasive aquatic macrophyte, water hyacinth {Eichhorniacrassipes (Mart.) Solm-Laubach: Pontedericeae}: problems and prospects. Res J Environ Sci 5:509–520. [6] Patel, S.,(2012). Threats, management and envisaged utilizations of aquatic weed Eichhorniacrassipes an overview. Rev Environ Sci Biotechnol (2012) 11:249–259. DOI 10.1007/s11157-012-9289-4. [7] Samuel, T., and Netsanet, A. (2014). Prevalence and Intensity of Water Hyacinth Infestation in the Water Bodies of Rift Valley, Ethiopia.
  • 5. Earth Sciences: an International Journal (ESIJ), Vol 1 No 1 5 [8] Tellez, T., Lopez, E., Granado, G., Perez, E., Lopez, R., and Guzman, J., (2008). The water hyacinth, Eichhorniacrassipes an invasive plant in the Guadiana River Basin (Spain). Aquatic Invasions 3, 42- 53. [9] UNEP, (2006). Africa Environment Outlook 2. Division of Early Warning and Assessment, United Nations Environment Programme, Nairobi. [10] UNEP, (2013). Global Environment Alert Service. Taking the pulse of the planet connecting science with policy, United Nation Environment Programme. [11] Zhang, Y., Zhang, D., Barrett, S., 2010. Genetic uniformity characterizes the invasive spread of water hyacinth (Eichhorniacrassipes), a clonal aquatic plant. Molecular Ecology 19: 1774-1786.