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Scientific registration n o. : 1768<br />

Symposium n o. : 29<br />

Presentation : Poster<br />

Growing halophytes in Egypt for forage production<br />

and desertification control<br />

Production fourragère et contrôle de la désertification<br />

en Egypte par la culture de plantes halophytes<br />

ASHOUR Nabih(1), ARAFAT Sayed(2), ABD EL-HALEEM Awad(3),<br />

SERAG Mamdoh(4), MANDOUR Safwat(5), MEKKI Bahaa(6)<br />

(1), (2), (3), (5), (6) National Research Centre, Dokki, Cairo, Egypt<br />

(4) Faculty of Science at Demietta, Mansoura Univ., Egypt.<br />

Introduction<br />

Egypt, like other developing countries of the arid and semi-arid regions, faces four<br />

major problems namely: (i) high rate of population increase (ii) limited natural resources<br />

of good quality water, (iii) existence of salt affected soil and (iv) shortage of food and<br />

feed. Therefore, studies should be oriented towards solving these problems and in<br />

particular to the management of salt affected soils. The cultivation of halophytic plants<br />

seems to be an ideal management practice of such soil types, when fresh water is not<br />

sufficient. Halophytes have attracted the attention of several workers in many countries<br />

(Aronson, 1989; Ashour, 1993 and Ashour and Thalooth (1993). Number of plant<br />

species have been screened for their productivity and/or nutritional potential when<br />

irrigated with saline water and even sea water (Glenn and O’Loary, 1985 and Gallagher,<br />

1985). Some halophytic species have been demonstrated as forage plants (Ashour et al.,<br />

1994 and Joshi et al., 1995).<br />

Therefore, the aim of this work was to investigate the growth response of some<br />

halophytic forage plants in coastal salt-affected soils by using diluted sea water for<br />

irrigation, in order to overcome the desertification as well as to solve the discharge of<br />

fresh water irrigation in Egypt.<br />

Materials and Methods<br />

Field trials were conducted during 1993-1996 seasons in the Saline Agriculture<br />

Experimental Station of the National Research Centre at Suez Gulf Coast to study the<br />

effect of salinity on growth and plant composition of five halophytic plants namely:<br />

Diplachne fusca, Spartina patens, Sporobolus virginicus (Smyrna-smooth), Sporobolus<br />

virginicus (Dixe-coarse) and Medicago sativa for comparison. Soil characteristics of the<br />

experimental site were as follows: pH 8.6, EC 1.2 dS.m -1 (1:1 W/V H2O), CaCO3 1.8%,<br />

sand 93.5%, silt 4.8% and clay 1.7%. Four salinity levels of diluted sea water being,<br />

12.5%, 25.0%, 37.5 and 50% were used in irrigation. Chemical characteristics of the<br />

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diluted sea water were determined using the methods described by the U.S. Salinity Lab.<br />

Staff (1954) and presented in Table (1).<br />

Table (1) Chemical characteristics of diluted sea water used in the Saline Agriculture<br />

Experimental Station at Suez Gulf Coast.<br />

Character Sea water proportion (%)<br />

12.5 25.0 37.5 50.0<br />

pH 8.0 8.0 8.1 8.1<br />

T.D.S. (g.L -1 ) 6.0 13.5 19.5 25.5<br />

Na (mg.L -1 ) 1910.0 3660.0 5470.0 7180.0<br />

K (mg.L -1 ) 54.6 117.0 172.0 217.0<br />

Ca (mg.L -1 ) 96.0 160.0 200.0 252.0<br />

Mg (mg.L -1 ) 216.0 420.0 593.0 806.0<br />

HCO3 (mg.L -1 ) 597.0 683.0 683.0 767.0<br />

Cl (mg.L -1 ) 3690 7460.0 10580.0 13490.0<br />

Each plant type was grown in four plots. Each plot was 4 m 2 and subjected to one<br />

of the salinity treatment.<br />

Several cuttings were taken from all tested plants during 12 months. Fresh weight of<br />

biomass was recorded. the harvested shoots were oven-dried at 65 o C, weighed, ground<br />

and analyzed for crude protein, fat and fibre, soluble carbohydrates and ash using the<br />

method of A.O.A.C. (1965).<br />

A field application was carried out to grow Diplachne fusca in salt affected soils<br />

(EC more than 17 dS.m -1 ) at the south coast of Qaroan Lack to emphasize the<br />

potentiality of this local halophyte as a forage crop under field conditions. Agricultural<br />

drainage water was used for irrigation (EC 2.8 dS.m -1 )<br />

Results and Discussion<br />

Effect of salinity on plant growth:<br />

Figure (1) shows that irrigation with diluted sea water affected the fresh and dry<br />

weights of biomass. Fresh and dry weights of the tested forage plants, except Medicago<br />

sativa increased by increasing the proportion of sea water in irrigation water from 12.5%<br />

to 25.0%. Further increase in salinity level in the irrigation water tended to decrease the<br />

fresh and dry weights of the forage halophytic plants. Yet even under 50% sea water in<br />

irrigation water the halophytic forage plants produced more than 50% of the fresh and<br />

dry weights as compared with control treatment (12.5%). The stimulatory effect of<br />

moderate salinity level on the growth of some halophytic plants was also reported by<br />

O’Leary (1988). Such growth stimulation at moderate salinity in halophytes may be<br />

attributed to improve shoot osmotic status as a result of increased ion uptake (Naidoo et<br />

al., 1995). Reduced growth at high salinities is probably associated with reduced turger<br />

and the high energy cost of massive salt secretion and osmoregualtion.<br />

Data also showed that all tested plant types tolerated diluted irrigation sea water up<br />

to 50% level. It was noticed that Sporobolus virginicus (Dixe) produced the highest<br />

biomass when the plants were irrigated with water containing either 25 or 37.5% sea<br />

water, followed by Spartina patens and Diplachne fusca. Sporobolus virginicus<br />

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(Smyrna) gave the lowest yield. However, Leith et al. (1994), conducted field<br />

experiments in the United Arab Emirates to grow the halophytic grass Sporobolus<br />

virginicus utilizing sea water of the Arabian Gulf. The results of their experiment<br />

indicated that Sporobolus virginicus has the ability to grow in highly saline environments<br />

which exceed even those found under our experiment.<br />

Effect of salinity on plant composition :<br />

The effect of salinity on the content of crude protein, fibre, fat and ash as well as,<br />

soluble carbohydrates of all tested forage halophytic plants are illustrated in Fig. (2).<br />

Increasing salinity level in the irrigation water tended to increase crude protein content<br />

while tended to decrease crude fiber. Crude fat and soluble carbohydrates contents<br />

seemed to be unaffected by changing the salinity level in the irrigation water. In this<br />

concern Leigh (1986) reported high crude protein content of several halophytic plants.<br />

He also speculated that halophytic plants could serve as valuable protein supplement to<br />

livestock when the associated grasses were dry and possibly protein deficient.<br />

Data also showed that Medicago sativa had relatively higher content of crude<br />

protein and lower soluble carbohydrates content. Diplachne fusca and Spartina patens<br />

contained a higher amount of soluble carbohydrates. The lowest crude fat content was<br />

recorded in Spartina patens. Whereas Sporobolus virginicus (Smyrna) and (Dixe) gave<br />

the highest ash content. At all levels of salinity concentration succulence of the tested<br />

halophytic plant types were more or less similar.<br />

Field application :<br />

Table (2) summarizes the change occurred in some chemical properties of saltaffected<br />

soil as result of Diplachne fusca cultivated for two growing seasons<br />

successively. Data showed that soluble salts markedly decreased after harvesting. The<br />

percent decrease in soluble salts was 34.5% in the surface layer. The most striking<br />

change was tremendous decrease in soluble Na and Cl. This phenomenon could be<br />

explained by the ability of halophytic plant to absorb high amounts of these elements.<br />

Table (2) Some chemical properties of salt-affected soil before planting and after<br />

harvesting of Diplachne fusca.<br />

pH EC Soluble cations and anions meq 100 g -1 soil<br />

dS.m -1<br />

Na K Ca Mg HCO3 Cl<br />

Before planting 8.0 17.4 63.6 0.75 15.0 11.0 9.0 67.2<br />

After harvesting 8.0 11.2 41.2 2.1 8.8 6.0 3.2 41.7<br />

Plant composition recorded in Table (3) show that Diplachne fusca grown in salt<br />

affected soil contained considerable amounts of crude protein, fibre, fat, soluble<br />

carbohydrates as well as nutritional elements. The high sodium content (2.14%) has not<br />

presented a problem to forage species due to the presences of specific internal osmotic<br />

adjustment mechanisms.<br />

3


Table (3) Fresh, dry weight and chemical composition of Diplachne fusca grown in salt<br />

affected soil at the south coast of Qaroan Lack.<br />

Character Value Character Value<br />

Fresh weight (ton acre -1 /year) 8.2 Phosphorus % 0.16<br />

Dry weight (ton acre -1 /year) 3.2 Calcium % 0.54<br />

Crude protein % 9.2 Magnesium % 0.40<br />

Crude fibre % 31.4 Potassium % 1.02<br />

Crude fat % 1.83 Sodium % 2.14<br />

Soluble carbohydrate % 42.9 K/Na ratio 0.48<br />

Ash % 14.7<br />

Therefore, Diplachne fusca seemed to be promising forage crops as well as to overcome<br />

the desertification problems particularly in arid and semi arid regions of Egypt.<br />

References<br />

A.O.A.C. (1965). Official Methods of Analysis of Association Analytical Chemists.<br />

Washington, D.C., 20044.<br />

Aronson, J.A. (1989). Haloph: a data base of salt tolerant plants of the world. Ed., E.<br />

Whitehead, Office of Arid Lands Studies, p. 77, Univ. Arizona, Tucson, Arizona,<br />

U.S.A.<br />

Ashour, N.I. (1993). Domestication of some useful halophytes under Egyptian<br />

conditions. Proc. IV. International Conf. Desert Development, 25-30 July 1993,<br />

Mexico City, Mexico, p. 170-181.<br />

Ashour, N.I. and Thalooth, A.T. (1993). Potentiality of growing halophytes by using<br />

hyper saline water. Meeting on Desertification & Soil Reclamation in Arab Gulf<br />

Countries Region, 22-25 Nov., 1993, El-Bahrain (In Arabic).<br />

Ashour, N.I., Serag, M.S. and Abd El-Haleem, A.K. (1994). Domestication and biomass<br />

production of Kochia scoparia (L.) Roth. as a fodder-producing halophyte under<br />

Egyptian conditions. J. Fac. Sci., U.A.E. Univ., 8: No. 8, 90-102.<br />

Gallagher, J. (1985). Halophytic crops for cultivation at sea water salinity. Plant and Soil<br />

89, 323-336.<br />

Glenn, E.P. and O’Leary, J.W. (1985). Productivity and irrigation requirements of<br />

halophytes grown with sea water in the Sonar Desert Journal of Aid Environments,<br />

9, 81-91.<br />

Joshi, A.J., Mab, B.S. and Hingalajia, H. (1995). Halophytes a good source of forage<br />

production under salt stressed conditions. I. Salvadora persica. In “Biology of Salt<br />

Tolerant Plants, Ed. M. Ajmal Khan and Irwin A. Ungar, Dept. Bot., Univ. Karachi,<br />

Karachi, Pakistan, p. 353-360.<br />

Leight, J.H. (1986). Forage value and utilization of chenopod dominated shrubland.<br />

Reclamation & Revegetation Research 5, 387-404.<br />

Lieth, A.F.; Shourbagy, M.N. and Abdel-Kader, M.H. (1994). Investigation of growth,<br />

ion accumulation and chlorophyll concentration of the halophytic grass Sporobolus<br />

virginicus (L.) Kunth in highly saline environments. Regional Environmental<br />

Symposium, U.A.E. Univ., Dec. 11-14, 1994.<br />

Naidoo, J.; Jahnke, J. and Von Willert, D.J. (1995). Gas exchange responses of the C14<br />

grass Sporobolus virginicus (Poaceae) to salinity stress. In Biology of Salt Tolerant<br />

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Plants. Ed. M. Ajmal Khan & Irwin A. Ungar, Dept. Bot., Univ. Karachi, Karachi,<br />

Pakistan, p. 121-130.<br />

O’Leary, J.W. (1988). Saline environments and halophytic crops. Proc. Intl. R and D.<br />

Conf., Arid Lands: Today and Tomorrow, Tucson, Arizona, U.S.A., Oct. 20-25<br />

(1985). Westview Press, Boulder, Colorado.<br />

U.S. Salinity Laboratory Staff (1954). Diagnosis and Improvement of Saline and Alkali<br />

Soils. U.S. Dept. of Agric. handbook No. 60.<br />

Key words : halophytes, salt-affected soil, sea water, forage production, desertification,<br />

Egypt<br />

Mots clés : halophytes, sols salés, eau de mer, production de forage, désertification,<br />

Egypte<br />

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