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A REVIEW OF THE UTILISATION OF WATER HYACINTH:
ALTERNATIVE AND SUSTAINABLE CONTROL
MEASURES FOR A NOXIOUS WEED
M. OJEIFO*, P.A. EKOKOTU**, N.F. OLELE**
and J. K. EKELEMU**
Department ofAgronorny, Forestry and Wildlife,
Delta State University, Asaba Gampus, Asaba.
* *Department

of Animal Science and Fisheries,
Delta State University, Asaba Campus, Asaba.

ABSTRACT
The global concern on the problem of the infestation of water bodies by
water hyacinth (Eichhornia crassipes) has provided the impetus for researchers
and other conceited bodies to exploit ways of controlling its spread. Generally,
efforts in this regard have been directed at the complete elimination of this weed
from our water bodies. It is believed that water hyacinth is potentially beneficial
to man, hence, this review was undertaken to highlight its possible application in
aqua-culture, bio-gas production, livestock feed, bin-fertilizer, waste water

treatment and as raw material for industries. It is suggested that cottage
industries be established in the affected conmiunities to translate these
possibilities into income earning sources. Thus, with institutional support from
government and non-governmental organisations, the water hyacinth menace
could be transformed from nuisance to wealth generation, employment and
poverty alleviation.

JNTRODUCTION
the tropics, aquatic weeds,
especially water hyacinth (Eichhornia
In

crassipes), affect man and his well-being
by impeding water flow in irrigation and
drainage canals, altering the oxygen level
of the water, thereby affecting fish and the
quality of water for domestic and
commercial usc. They also hinder or

completely prevent navigation of river
systems, encourage the build-up of snails,
which are essential ii terrnediate host for

bilharzia organisms and liver-flukes, and
provide or enhance breeding places for
certain disease-carrying mosquitoes (Bennett and Woodford, 1978).

In spite of these problems, a critical
study of the plant physiology indicated
that it could have potential application in
agriculture and in homes. There must be a

concerted effort therefore, at harnessing
this beneficial biological resource rather

than just spending huge financial and
human resources at just eradicating it.

71
The 'beautiful blue devil' water hya-

Coupled with the near stable nature of

cinth, recognizable by its lavender flowers

the tropical environment, the plant is
euryhaline, tolerating both fresh and
marine waters, hence its spread knows no

and shinning bright leaves is a prolific
aquatic plant, which spreads at an alarming rate. The weed has adapted itself
exceedingly well to almost every area in
which it has been introduced. It has an
extremely high growth rate, propagates
itself vegetatively and sexually. Its rapid
proliferation often results in the clogging
of drains and can interfere with shipping,
recreational aStivities and the movement
of water. Tyagarajan (1983 a) reported

boundaries. Further to this, man through
his activities such as discharge of wastewater, industrial effluents, run-off from
land into the water systems, has greatly

altered the hydrological regime of the
waters thereby increasing the nutritive
level of the aquatic environment which
favours the growth and spread of the plant.

that one hectare pond of water hyacinth
will produce 0.9 to 1.8t of dry matter per

APPLICATION IN AQUACULTURE

It grows rapidly in water with

in Nigeria is the practice whereby fish

temperatures of between 28 and 30°C and
with a pH of 4.0 - 8.0, and ceases to grow
when the water temperature is above 30°C
or below 10°C. The weed dies when the
tip rhizome is frozen.

farmers allow controlied growth of water
hyacinth in their fish ponds. Evidently,
such plant is employed to provide shade
against the scorching effects of sunlight
during the day, as well as offering
protection for the young fish against
predators. Similarly, water hyacinth is

day.

The weights and proportions of water
hyacinth differ considerably in different
samples collected in various seasons.

However, the typical green plant consists

of 24.8 percent root, 41.9 percent stalk,
and 33.3 percent leaf (Thyagarajan, 1983).
Only the stalk portion of the plant is used
for the manufacture of paper-board.

ORIGIN AND DISTRIBUTION
Eichhornia crass ipes is one of the
world's major free-floating aquatic

macrophytçs with long hanging roots in
water. Early records of its presence in
River Nile was in the later part of the 18th
Century (Garry, et al, 1997). The plant

now circum-globed in tropical and subtropical regions, was first noticed in
Nigerian waters, on the shore of Lagos
lagoon in October 1984 (Ekelemu 1998),
but has since spread to other parts of the
country, particularly in the Coastal states.

A common observation in recent times

used as a substrate for the deposition of
eggs by spawning brood-stocks especially

for the production of ornamental fish.
Scores of water hyacinth are introduced
into the spawning ponds especially for the
production of ornamental fish. Thereafter,
the brood fish are put into the pond.. After
spawning, the water hyacinth is removed

with the eggs adhering to the roots The
whole plants with the eggs are incubated
in the hatchery.
After hatching, the
hatchhings detach from the root system of
the weed and swim freely. At this stage,
the weed is removed from the ponds.

APPLICATION IN BIOLOGICAL
WAST1 WATER TREATMENT
The application of water hyacinth for

waste water treatment in Nigeria,

is

gradually gaining ground.
Ogunlade
(1992) reported its potentials as a mopping

agent and scavenger of heavy and toxic

72
in industrial and domestic
effluents. Akobundu (1987) reported the

elements

use of water hyacinth for waste water
treatment by some agencies. The capacity

of this plant to purif' water rests on its
ability to vigorously extract nutrients from
its medium.
Laboratory analysis has

shown that water hyacinth is of a high

with its capacity to extract nutrients

efficiently from its medium makes it a
good candidate for the purification of
turbid and polluted waters. However, it
should be curtailed to prevent dispersal
beyond the area of application.

A RAW MATERIAL FOR BlO-GAS

absorptive capacity (Soerjani, 1984).
Although it is relatively poorer in

]3io-gas technology requires large amount
and continuous supply of vegetative

extraction of nutrient compounds when
compared to water lettuce and guinea

materials for the production of methane
which can be used directly in homes for

grass (Table 1), it functions as an effective

cooking and heating arid even in
agriculture for drying or converted to
other sources of energy, such as

mopping aent and scavenger of heavy
metals like cadmium, mercury, and nickel.
And also its extraction of other chemical

substances such as nitrates, phosphates,
ammonia, silicate, chlorine and sulphur

deposited in the aquatic habitat from
industrial and domestic effluent is
remarkable (Ogunlade, 1992). Its vigorous

growth and repeated cultivation coupled

electricity. The menace of aquatic weeds
such as E. crassipes could be converted to
an economic resource for the welfare of
man. This process will go a long way in
ameliorating the threat posed by the
incursion of water hyacinth into our water
bodies.

Table 1. Analysis Of Water Hyacinth, Water Lettuce And
Guinea Grass For Eight Different Minerals
Sample

Mineral

Water hyacinth

Water lettuce

Concentration (ppm)
Calcium (Ca)

1,808 —

Guinea
grass

6,594

4,545

Phosphorus(P)

791

1,108

3,030

Potassium (K)

46,060

72,524

2,257

Magnesium (Mg)

3,114

3,305

2,952

Sodium (Na)

3,784

2,043

174

222

156

212

2,557

6,717

213

20

31

26

Manganese (Mn)
Iron (Fe)

Copper (Cu)

Source: Aderibighe and Brown (1993)

73

—
The utilization of water hyacinth
through bio-gas production is a

used directly

household slogan in Porto-Novo, Benin
Republic. This activity is a sustainable

waste from biogas generation as
indicated above can also be collected for

alternative which is the most costeffective endeavour of tremendous
benefit in all communities where this
weed abounds (Tobor, 1994). Biogas

use directly on the farm. Alternatively,

production is most appropriately termed
Biomethanogenesis (National Academy
of Sciences 1987). This term was given

birth to due to the high amount of
methane (40 — 65%) produced during
the digestion process.
scale,

Soerjani

(1984)

has

suggested that a digester of 6 in3 in
dimension be loaded with a mixture of
shredded water hyacinth (stems) and
10% by weight of cattle dung. The
temperature of 30 — 35°C at pH of 7.0 —
7.5
is maintained for maximum
production. This set-up is left for one
week before the production of gas

commences and continues for the next
four weeks. Approximately, 2.0m3/day

of the gas produced was used on a
burner for 3 hours or in a gas lamp for 6
hours. Pig dung produced 7.0m3 while

poultry dung yielded 29.4m3. It has
been recommended that ferro-cement

gives a better yields of this gas and
should be used. However, other types of
digesters include French, Chinese,
Indian and Trans-mulched.
AS RAW MATERIAL FOR BlO-

FERTILIZER
Bio-fertilizer is acclaimed to be a
sustainable source of plant nutrient due
to its improvement of soil structure as
well as the slow release of the nutrients.
The biomass of water hyacinth can be

green manure as

these materials could be mixed with
other organic materials before use.
The practice is popular among
farmers around the aquatic habitats
where water hyacinth abounds. The

waste products (slurry) coming from
biogas production is collected regularly

and used for growing maize, peanuts,
soybean and cassava.

For the production of this gas on a
small

as

compost. Also, the digested vegetative

The coarse powder obtained from
the root of water hyacinth has
effectively been used to aid crop

production in economic crops such as
vegetables

(Chakraverty,

1983;

Oso,

1988). Because of the high moisture
content Df this plant, it was reported to
increase the moisture holding capacity
of the soil while promoting good
adhesion to seeds.
In
whatever
condition, water hyacinth is used, it may
be necessary to do mineral analysis to
guard against the pollution by potential
uptake of heavy metals.

AS RAW MATERIAL FOR LOCAL
INDUSTRIES
Akobundu (1987) reported that aquatic
weed, can serve as raw material for pulp
and paper, fibre for making chairs, mats
and baskets. It can also be used as
thatch. However, their application has
not received the required attention.
Healey (1994) observed that the
enormous biomass of water hyacinth has
stimulated many attempts at its
utilization. He further reported that it
has limited
application in the
manufacture of poor quality paper,

74
biogas generation, effluent treatment
and certain handicraft. Research could

improve on the existing infonnation at
converting the raw material of water
hyacinth into industrial products. This
feed the industries. The whole process
could generate employment and alleviate

attempted and this will go a long way in
stimulating community participation by
reducing the nuisance created by water

hyacinth, when continuous harvest is
made
and
manufacturing
units
located in all places where water hyacinth
is available in abundance and free of cost.

poverty in the affected areas.

POTENTIALS AS A FEEDSTUFF

Thyagaraja (1983) demonstrated how

the stalks of water hyacinth could be
pulped,.

and

converted

into

medium

quality papers/boards such as cardboard
and coloured cards/cover papers. Such
puips should however be blended with
long fibrous puips such as cotton rags and
waste paper puips to minimize the
shrinkage of paper during drying.
However, the manufacture of bond and
other high quality paper is not

economically viable owing to the low
yields of water hyacinth pulp. Even for
the manufacture of medium quality
paper/boards Thyagaraja (1983) advised

The dearth of animal protein with
increasing cost of food production coupled

with rapid population growth necessitate
the search for non-conventional sources of
protein such as leaf protein concentrate
(LPC) from water hyacinth (Ogunlade et
al 1988). The plant in combination with
concentrate of other feeds has proved to
be

a good quality protein source for

animal feed (Igbinosun and Talabi, 1982).

When compared with conventional
NIOMR feeds, dried water hyacinth was
found to be a suitable artificial feeds for

the culture of tilapia (Tables 2 and 3).

that the manufacturing unit should be
Table 2. Proximate composition (%) of NIOMR flsli feed and dried water hyacinth.
Components

NIOMR Feed

Water Hyacinth

Crude Protein

38.5

14.2

Crude Fibre

9.0

20.4

-

3.3

Lipids

6.8

-

Moisture

13,4

10.4

Others

32.3

-

Ash

-

27.2

N-Free extract

-

24.6

Crude Fat

Source: Igbinosun and Talabi (1982).

75
Table 3: Growth Increase (%) Of Tilapia Fed With NIOMR Feed And Water
Hyacinth (Based On Table 2) Over Eight Week Period
NIOMR feed

Dried water hyacinth

Weight increase

49.5

22.2

Length increase

15.4

5.5

Food Conversion ratios

6.61

12.90

Source: KusemUu and Akingboju (1998)
Some other documented research
findings have indicated that water

scope in the present practice and the

hyacinth has great potentials as animal
feed source (Tables 3 and 4). It has a
reasonable amount of crude protein
content, and compares more favourably

substantial enough to meet the control

quantity

potentially

utilized

is

not

target.

Adenbigbe and Brown (1993) have
demonstrated that the nutr tive value as
well as nutrient digestibi Ity of water
hyacinth is enhanced when dried and

with guinea grass that has enjoyed
widespread use as silage to feed livestock.

.

Pig can consume 1 2kg fresh weight of

supplemented with high

Water hyacinth daily. The dried, crushed
percentages, 2.5 — 10% with the ordinary

ingredient and a suitable protein source
(Table 5). Thus, water hyacinth though
now a foe, is a potential saviour of the

feed for pig, chicken, ducks, cow and

animal feed industry that is currently

rabbits (Soerj ani, 1984). This has limited

groaning under high cost of feedstuff.

ones are used in mixtures of various

energy feed

TABLE 4: Composition of water 1iyaiut1i and guinea grass
Water hyacinth

Guinea grass

Dry matter (DM.%)

10.2

33.1

Gross energy (KcalIg of DM)

2.2

3.5

Organic matter (OM)

57.0

89.4

Crude Protein (CP)

11.3

6.7

Crude Fibre

(CF)

11.7

30.2

Ether Extract (EE)

3.4

4.4

Ash

43.0

10.6

Nitrogen Free Extract

30.6

48.1

Analysis of DM (%,)

Source: Aderibigbe and Brown (1993).

76
Table 5: Crude Protein (%) of Water Hyacinth and Guinea Grass Silage
Supplemented With Different Nitrogen Sources and Various Levels of Maize
Level of Maize

Guinea grass

Water hyacinth
Groundnut cake

Blood meal

Groundnut
cake

Blood meal

0

18.3

18.1

14.6

14.9

10

18.9

18.8

16.4

15.1

20

18.5

17.0

14.1

15.1

%Digestibility

45.3

58.4

41.4

25.9

-

Source: ('Aderibigbe and Brown, 1993)

CONCLUSION

option.

The threat of water hyacinth to aquatic
ecosystems is real. The infestation of our

water bodies by this aquatic weed is a
scourge that must be tackled with all
amount of seriousness. However, the
current drive towards the total eradication

of the weed may not be the most viable
option, for the reason of high cost and the
fact that some of the eradication methods
may do further harm to the environment.

In the face of today's economic stress
militating against mankind, the costs of
basic input resources have gone beyond

the reach of ordinary people.

Water
hyacinth, which is seen as a nuisance and

combated at huge economic costs
resource-poor

economies,

may

to

Some of these probable benefits

have been articulated and advocated.
However, the realization of these
objectives may truly be possible if there is
institutional support from the government
and
non-governmental
organisations

NGO's) in the form of establishment of
pilot programmes or cottage industries to
translate some of these potential benefits
income
into
generating
ventures.
Additional institutional support could also
be in the form of research grants, public
enlightenment of local communities,
extension services, on existing technology
on the utilization of water hyacinth, and
capacity building for potential operators of
the industry.
This could create
employment, and alleviate poverty.

well

become the cornerstone of raw-material
production to the growing industries. The
potentials outlined have good promises
particularly for a growing economy. The
international efforts to rid the water bodies
of water hyacinth deserves commendation

but the need to turn its menace into a
blessing for the populace, in our opinion,
will certainly receive a wider support.

Thus, the exploitation of means by
which this plant could be harnessed and
put into profitable use may sound a viable

77

REFERENCES
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hyacinth Eichhornia crassipes) through
biogas production at Port Novo, Republic of
Benin (In press).

Aderibigbe, A.O. and A.A. Brown, (1993)
Nutritive characteristics of two tropical aquatic
weeds for ruminants.
Ife
Agriculture, 16 & 17: 42-54.

Journal of

Akobundu, 1.0. (1987). Weed Science in the
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Inter-Science Publication. John Wiley & Sons
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Akobundu, 1.0. and C.W. Agyakwa (1987). A
handbook ctf West African Weeds. International
Institute of Tropical Agriculture. Ibadan,
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Barrett S.G.T. and LW. Forno (1982).

Style

morph distribution in new world populations of
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and EJ(.
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Bennett,

F.D.

Woodford, (1978).
in:
in the Tropics.

National Academy of Science (1987). In: Making
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Ogunlade, V. (1992) Chemical and nutritional
evaluation of water hyacinth in Nigerian
.

waterways. Ph.D Thesis. Obafemi Awolowo
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Oguniade, Y. Afolabi, 0.A., Osuntogun O.A. and
Oke, 0.L. (1988) Extraction of protein from
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The Proceedings
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Weeds and their control in the humid and sub—

humid tropics. Proceedings of a conference
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Ekelernu J.K. (1998).
water
inhabitin'

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hyacinth
(Eichhornia

crassipes) in Benin River, Southern Nigeria,
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Garry, H. J. Waage and C. Phiri. (1997). The
water hyacinth problem in Tropical Africa.

Meeting f International Water

Hyacinth

Consortium held at World Bank, Washington,

Oso, B.A. (1988) Invasion of Nigeria waterways by
water hyacinth: Ecological and Biological
Observation.
The
Proceedings
of the
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Rahman A.T.M.F., C.0. Akucshi, and A.!.
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Eichhoi-nia crassipes and Azolla africana.
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Communications. Faculty of Natural Sciences,
University of Jos, Nigeria.
Faculty

18-19 March, 1997.

lgbinosuii, J.E and Talabi S.0. (1982) Studies on
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the 2nd Conference of Fisheries Society of

Reddy K.R.M. Agami, E.P.M. Angelo and JC.
Tucker (1991) Influence of Potassium on
growth and nutrient storage by water hyacinth.
B/a jesource Technology 37:79-84.

Nigeria, Ca!abar, 24-27 Jan, 1982.

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K.

Comparative

and Akingboju
growth
of

S.O. (1988).
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melanothejon (Ruppell) on formulated fish
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and

water

hyacinth

diets.

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Labrada, R. Caseley J.C. and Parker C. (1994)
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Soerjani, M. (1984) Indonesia experience in water
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78
Water Hyacinth Control Measures for a Noxious Weed

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Water Hyacinth Control Measures for a Noxious Weed

  • 1. A REVIEW OF THE UTILISATION OF WATER HYACINTH: ALTERNATIVE AND SUSTAINABLE CONTROL MEASURES FOR A NOXIOUS WEED M. OJEIFO*, P.A. EKOKOTU**, N.F. OLELE** and J. K. EKELEMU** Department ofAgronorny, Forestry and Wildlife, Delta State University, Asaba Gampus, Asaba. * *Department of Animal Science and Fisheries, Delta State University, Asaba Campus, Asaba. ABSTRACT The global concern on the problem of the infestation of water bodies by water hyacinth (Eichhornia crassipes) has provided the impetus for researchers and other conceited bodies to exploit ways of controlling its spread. Generally, efforts in this regard have been directed at the complete elimination of this weed from our water bodies. It is believed that water hyacinth is potentially beneficial to man, hence, this review was undertaken to highlight its possible application in aqua-culture, bio-gas production, livestock feed, bin-fertilizer, waste water treatment and as raw material for industries. It is suggested that cottage industries be established in the affected conmiunities to translate these possibilities into income earning sources. Thus, with institutional support from government and non-governmental organisations, the water hyacinth menace could be transformed from nuisance to wealth generation, employment and poverty alleviation. JNTRODUCTION the tropics, aquatic weeds, especially water hyacinth (Eichhornia In crassipes), affect man and his well-being by impeding water flow in irrigation and drainage canals, altering the oxygen level of the water, thereby affecting fish and the quality of water for domestic and commercial usc. They also hinder or completely prevent navigation of river systems, encourage the build-up of snails, which are essential ii terrnediate host for bilharzia organisms and liver-flukes, and provide or enhance breeding places for certain disease-carrying mosquitoes (Bennett and Woodford, 1978). In spite of these problems, a critical study of the plant physiology indicated that it could have potential application in agriculture and in homes. There must be a concerted effort therefore, at harnessing this beneficial biological resource rather than just spending huge financial and human resources at just eradicating it. 71
  • 2. The 'beautiful blue devil' water hya- Coupled with the near stable nature of cinth, recognizable by its lavender flowers the tropical environment, the plant is euryhaline, tolerating both fresh and marine waters, hence its spread knows no and shinning bright leaves is a prolific aquatic plant, which spreads at an alarming rate. The weed has adapted itself exceedingly well to almost every area in which it has been introduced. It has an extremely high growth rate, propagates itself vegetatively and sexually. Its rapid proliferation often results in the clogging of drains and can interfere with shipping, recreational aStivities and the movement of water. Tyagarajan (1983 a) reported boundaries. Further to this, man through his activities such as discharge of wastewater, industrial effluents, run-off from land into the water systems, has greatly altered the hydrological regime of the waters thereby increasing the nutritive level of the aquatic environment which favours the growth and spread of the plant. that one hectare pond of water hyacinth will produce 0.9 to 1.8t of dry matter per APPLICATION IN AQUACULTURE It grows rapidly in water with in Nigeria is the practice whereby fish temperatures of between 28 and 30°C and with a pH of 4.0 - 8.0, and ceases to grow when the water temperature is above 30°C or below 10°C. The weed dies when the tip rhizome is frozen. farmers allow controlied growth of water hyacinth in their fish ponds. Evidently, such plant is employed to provide shade against the scorching effects of sunlight during the day, as well as offering protection for the young fish against predators. Similarly, water hyacinth is day. The weights and proportions of water hyacinth differ considerably in different samples collected in various seasons. However, the typical green plant consists of 24.8 percent root, 41.9 percent stalk, and 33.3 percent leaf (Thyagarajan, 1983). Only the stalk portion of the plant is used for the manufacture of paper-board. ORIGIN AND DISTRIBUTION Eichhornia crass ipes is one of the world's major free-floating aquatic macrophytçs with long hanging roots in water. Early records of its presence in River Nile was in the later part of the 18th Century (Garry, et al, 1997). The plant now circum-globed in tropical and subtropical regions, was first noticed in Nigerian waters, on the shore of Lagos lagoon in October 1984 (Ekelemu 1998), but has since spread to other parts of the country, particularly in the Coastal states. A common observation in recent times used as a substrate for the deposition of eggs by spawning brood-stocks especially for the production of ornamental fish. Scores of water hyacinth are introduced into the spawning ponds especially for the production of ornamental fish. Thereafter, the brood fish are put into the pond.. After spawning, the water hyacinth is removed with the eggs adhering to the roots The whole plants with the eggs are incubated in the hatchery. After hatching, the hatchhings detach from the root system of the weed and swim freely. At this stage, the weed is removed from the ponds. APPLICATION IN BIOLOGICAL WAST1 WATER TREATMENT The application of water hyacinth for waste water treatment in Nigeria, is gradually gaining ground. Ogunlade (1992) reported its potentials as a mopping agent and scavenger of heavy and toxic 72
  • 3. in industrial and domestic effluents. Akobundu (1987) reported the elements use of water hyacinth for waste water treatment by some agencies. The capacity of this plant to purif' water rests on its ability to vigorously extract nutrients from its medium. Laboratory analysis has shown that water hyacinth is of a high with its capacity to extract nutrients efficiently from its medium makes it a good candidate for the purification of turbid and polluted waters. However, it should be curtailed to prevent dispersal beyond the area of application. A RAW MATERIAL FOR BlO-GAS absorptive capacity (Soerjani, 1984). Although it is relatively poorer in ]3io-gas technology requires large amount and continuous supply of vegetative extraction of nutrient compounds when compared to water lettuce and guinea materials for the production of methane which can be used directly in homes for grass (Table 1), it functions as an effective cooking and heating arid even in agriculture for drying or converted to other sources of energy, such as mopping aent and scavenger of heavy metals like cadmium, mercury, and nickel. And also its extraction of other chemical substances such as nitrates, phosphates, ammonia, silicate, chlorine and sulphur deposited in the aquatic habitat from industrial and domestic effluent is remarkable (Ogunlade, 1992). Its vigorous growth and repeated cultivation coupled electricity. The menace of aquatic weeds such as E. crassipes could be converted to an economic resource for the welfare of man. This process will go a long way in ameliorating the threat posed by the incursion of water hyacinth into our water bodies. Table 1. Analysis Of Water Hyacinth, Water Lettuce And Guinea Grass For Eight Different Minerals Sample Mineral Water hyacinth Water lettuce Concentration (ppm) Calcium (Ca) 1,808 — Guinea grass 6,594 4,545 Phosphorus(P) 791 1,108 3,030 Potassium (K) 46,060 72,524 2,257 Magnesium (Mg) 3,114 3,305 2,952 Sodium (Na) 3,784 2,043 174 222 156 212 2,557 6,717 213 20 31 26 Manganese (Mn) Iron (Fe) Copper (Cu) Source: Aderibighe and Brown (1993) 73 —
  • 4. The utilization of water hyacinth through bio-gas production is a used directly household slogan in Porto-Novo, Benin Republic. This activity is a sustainable waste from biogas generation as indicated above can also be collected for alternative which is the most costeffective endeavour of tremendous benefit in all communities where this weed abounds (Tobor, 1994). Biogas use directly on the farm. Alternatively, production is most appropriately termed Biomethanogenesis (National Academy of Sciences 1987). This term was given birth to due to the high amount of methane (40 — 65%) produced during the digestion process. scale, Soerjani (1984) has suggested that a digester of 6 in3 in dimension be loaded with a mixture of shredded water hyacinth (stems) and 10% by weight of cattle dung. The temperature of 30 — 35°C at pH of 7.0 — 7.5 is maintained for maximum production. This set-up is left for one week before the production of gas commences and continues for the next four weeks. Approximately, 2.0m3/day of the gas produced was used on a burner for 3 hours or in a gas lamp for 6 hours. Pig dung produced 7.0m3 while poultry dung yielded 29.4m3. It has been recommended that ferro-cement gives a better yields of this gas and should be used. However, other types of digesters include French, Chinese, Indian and Trans-mulched. AS RAW MATERIAL FOR BlO- FERTILIZER Bio-fertilizer is acclaimed to be a sustainable source of plant nutrient due to its improvement of soil structure as well as the slow release of the nutrients. The biomass of water hyacinth can be green manure as these materials could be mixed with other organic materials before use. The practice is popular among farmers around the aquatic habitats where water hyacinth abounds. The waste products (slurry) coming from biogas production is collected regularly and used for growing maize, peanuts, soybean and cassava. For the production of this gas on a small as compost. Also, the digested vegetative The coarse powder obtained from the root of water hyacinth has effectively been used to aid crop production in economic crops such as vegetables (Chakraverty, 1983; Oso, 1988). Because of the high moisture content Df this plant, it was reported to increase the moisture holding capacity of the soil while promoting good adhesion to seeds. In whatever condition, water hyacinth is used, it may be necessary to do mineral analysis to guard against the pollution by potential uptake of heavy metals. AS RAW MATERIAL FOR LOCAL INDUSTRIES Akobundu (1987) reported that aquatic weed, can serve as raw material for pulp and paper, fibre for making chairs, mats and baskets. It can also be used as thatch. However, their application has not received the required attention. Healey (1994) observed that the enormous biomass of water hyacinth has stimulated many attempts at its utilization. He further reported that it has limited application in the manufacture of poor quality paper, 74
  • 5. biogas generation, effluent treatment and certain handicraft. Research could improve on the existing infonnation at converting the raw material of water hyacinth into industrial products. This feed the industries. The whole process could generate employment and alleviate attempted and this will go a long way in stimulating community participation by reducing the nuisance created by water hyacinth, when continuous harvest is made and manufacturing units located in all places where water hyacinth is available in abundance and free of cost. poverty in the affected areas. POTENTIALS AS A FEEDSTUFF Thyagaraja (1983) demonstrated how the stalks of water hyacinth could be pulped,. and converted into medium quality papers/boards such as cardboard and coloured cards/cover papers. Such puips should however be blended with long fibrous puips such as cotton rags and waste paper puips to minimize the shrinkage of paper during drying. However, the manufacture of bond and other high quality paper is not economically viable owing to the low yields of water hyacinth pulp. Even for the manufacture of medium quality paper/boards Thyagaraja (1983) advised The dearth of animal protein with increasing cost of food production coupled with rapid population growth necessitate the search for non-conventional sources of protein such as leaf protein concentrate (LPC) from water hyacinth (Ogunlade et al 1988). The plant in combination with concentrate of other feeds has proved to be a good quality protein source for animal feed (Igbinosun and Talabi, 1982). When compared with conventional NIOMR feeds, dried water hyacinth was found to be a suitable artificial feeds for the culture of tilapia (Tables 2 and 3). that the manufacturing unit should be Table 2. Proximate composition (%) of NIOMR flsli feed and dried water hyacinth. Components NIOMR Feed Water Hyacinth Crude Protein 38.5 14.2 Crude Fibre 9.0 20.4 - 3.3 Lipids 6.8 - Moisture 13,4 10.4 Others 32.3 - Ash - 27.2 N-Free extract - 24.6 Crude Fat Source: Igbinosun and Talabi (1982). 75
  • 6. Table 3: Growth Increase (%) Of Tilapia Fed With NIOMR Feed And Water Hyacinth (Based On Table 2) Over Eight Week Period NIOMR feed Dried water hyacinth Weight increase 49.5 22.2 Length increase 15.4 5.5 Food Conversion ratios 6.61 12.90 Source: KusemUu and Akingboju (1998) Some other documented research findings have indicated that water scope in the present practice and the hyacinth has great potentials as animal feed source (Tables 3 and 4). It has a reasonable amount of crude protein content, and compares more favourably substantial enough to meet the control quantity potentially utilized is not target. Adenbigbe and Brown (1993) have demonstrated that the nutr tive value as well as nutrient digestibi Ity of water hyacinth is enhanced when dried and with guinea grass that has enjoyed widespread use as silage to feed livestock. . Pig can consume 1 2kg fresh weight of supplemented with high Water hyacinth daily. The dried, crushed percentages, 2.5 — 10% with the ordinary ingredient and a suitable protein source (Table 5). Thus, water hyacinth though now a foe, is a potential saviour of the feed for pig, chicken, ducks, cow and animal feed industry that is currently rabbits (Soerj ani, 1984). This has limited groaning under high cost of feedstuff. ones are used in mixtures of various energy feed TABLE 4: Composition of water 1iyaiut1i and guinea grass Water hyacinth Guinea grass Dry matter (DM.%) 10.2 33.1 Gross energy (KcalIg of DM) 2.2 3.5 Organic matter (OM) 57.0 89.4 Crude Protein (CP) 11.3 6.7 Crude Fibre (CF) 11.7 30.2 Ether Extract (EE) 3.4 4.4 Ash 43.0 10.6 Nitrogen Free Extract 30.6 48.1 Analysis of DM (%,) Source: Aderibigbe and Brown (1993). 76
  • 7. Table 5: Crude Protein (%) of Water Hyacinth and Guinea Grass Silage Supplemented With Different Nitrogen Sources and Various Levels of Maize Level of Maize Guinea grass Water hyacinth Groundnut cake Blood meal Groundnut cake Blood meal 0 18.3 18.1 14.6 14.9 10 18.9 18.8 16.4 15.1 20 18.5 17.0 14.1 15.1 %Digestibility 45.3 58.4 41.4 25.9 - Source: ('Aderibigbe and Brown, 1993) CONCLUSION option. The threat of water hyacinth to aquatic ecosystems is real. The infestation of our water bodies by this aquatic weed is a scourge that must be tackled with all amount of seriousness. However, the current drive towards the total eradication of the weed may not be the most viable option, for the reason of high cost and the fact that some of the eradication methods may do further harm to the environment. In the face of today's economic stress militating against mankind, the costs of basic input resources have gone beyond the reach of ordinary people. Water hyacinth, which is seen as a nuisance and combated at huge economic costs resource-poor economies, may to Some of these probable benefits have been articulated and advocated. However, the realization of these objectives may truly be possible if there is institutional support from the government and non-governmental organisations NGO's) in the form of establishment of pilot programmes or cottage industries to translate some of these potential benefits income into generating ventures. Additional institutional support could also be in the form of research grants, public enlightenment of local communities, extension services, on existing technology on the utilization of water hyacinth, and capacity building for potential operators of the industry. This could create employment, and alleviate poverty. well become the cornerstone of raw-material production to the growing industries. The potentials outlined have good promises particularly for a growing economy. The international efforts to rid the water bodies of water hyacinth deserves commendation but the need to turn its menace into a blessing for the populace, in our opinion, will certainly receive a wider support. Thus, the exploitation of means by which this plant could be harnessed and put into profitable use may sound a viable 77 REFERENCES Adekoya BJ3. (2000) Enhanced utilization of water hyacinth Eichhornia crassipes) through biogas production at Port Novo, Republic of Benin (In press). Aderibigbe, A.O. and A.A. Brown, (1993) Nutritive characteristics of two tropical aquatic weeds for ruminants. Ife Agriculture, 16 & 17: 42-54. Journal of Akobundu, 1.0. (1987). Weed Science in the Tropics: Principle and Practices. A Wiley Inter-Science Publication. John Wiley & Sons New York.
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