Urban Development Threatening Wild Plants in Doha City-Qatar: Ecophysiology is a Prerequisite for Ecological Restoration
Rapid disappearing of many coastal and inland habitats in the State of Qatar, due to the enormous activities of constructions, would put wildlife at real risk; urging scientists for environment conservation. This study was aimed to document the morphological features and the ecophysiological aspects of four wild plant species, Aeluropus lagopoides, Sporobolus spicatus, Ochradenus baccatus and Tetraena qatarense. Analyses included physical and chemical properties of soils and organic and inorganic contents of these plants were carried out. Although these plants are considered as xerophytes as the data of soil water content have shown; they might have well adapted to saline environments, since they live in soils of high salinity levels. A. lagopoides, S. spicatus and T. qatarense were living in soils of ECe ranged between 45 to 50 dS m-1, between 107 to 128 dS m-1 and between 12 to 187 dS m-1 respectively. O. baccatus, on the other hand, proved to be a typical xerophyte plant since it was never found in saline soils and survived water deficit as low as 4-12% field capacity. Considerable variations were found in all parameters studied especially in the electrical conductivity of the saturated soil extracts (ECe). Also, these species showed great variation in the organic components especially proline, soluble sugars and nitrogen, photosynthetic pigments and major elements. The data of trace elements, however, did not indicate clear differences. Such efforts can be considered as a prerequisite for successful ecological restoration, encouraging the decision makers to implement plans for restoration of vegetation.
Received: May 26, 2011;
Accepted: June 17, 2011;
Published: December 03, 2011
The State of Qatar has become an important international center for various
activities, political, sports, social, etc which requires tremendous expansion
in the infrastructure of various aspects of the civil life (Richer,
2008). Recent reports have shown that the wildlife, environment, ecosystem
services and biodiversity in the State of Qatar are under real threat. This
is because of the industrial development and expansions in the activities of
oil and gas industry which are accompanied with enormous urban constructions
in various areas especially in Doha city (Yasseen and Al-Thani,
2007; Yasseen and Abu-Al-Basal, 2008, 2010).
Scientific solutions to minimize the impact of the new developments on the environment
were strongly suggested and urgently needed. Thus, efforts should start with
the recording and documenting the existing wildlife and plants and their ecophysiology
under their natural habitats. Such efforts can be considered as a prerequisite
for successful ecological restoration (Al-Ansi et al.,
2004; Abdel-Bari et al., 2007; Yasseen
and Abu-Al-Basal, 2010). Moreover, it would be very useful to improve the
awareness and comprehend the importance of wild plants under their natural habitats.
One most important reason for studying sites around Doha, their plant cover
and the life they support, is the fast rate at which many habitats are disappearing
specifically in Doha and also in a number of other areas in the State of Qatar.
Some practical measures were suggested for the local authorities to maintain
the environment and to solve the problems and difficulties facing such efforts
(Al-Ansi et al., 2004; Flowers,
2004; Abdel-Bari et al., 2007; Richer,
2008; Yasseen and Abu-Al-Basal, 2010). Moreover,
many wild plants living in the State of Qatar have been considered as economic
and medicinal plants (Shabana et al., 1990; Rizk
and El-Ghazaly, 1995; Al-Easa et al., 2003),
as well as addressing very important topics in biology (Sage,
2002; Lara et al., 2006; Boyd
et al., 2007; Mohsenzadeh et al., 2006).
Some halophytes can be exploited in saline and sodic soils to achieve ecological
recovery (Guan et al., 2010). These plants can
be considered as good sources of salt and drought resistant traits from which
genes can be manipulated (Flowers, 2004; Yasseen
and Al-Thani, 2007) and of which some anatomical, physiological and biochemical
features are consistently associated with the resistance to stress conditions
(Yasseen et al., 2010). The Arabian Gulf States
with their comparatively superior financial status may be leaders in the technological
research in salinity and drought stresses (Abdel-Bari et
al., 2007; Yasseen and Abu-Al-Basal, 2010).
Therefore, the present work focuses on four wild xerophytic species belonging
to three families; two species Aeluropus lagopoides and Sporobolus
spicatus, belong to Gramineae and Ochradenus baccatus from Resedaceae
and Tetraena qatarense from Zygophyllaceae. Therefore, this study was
carried out to document the morphological features and the ecophysiological
aspects of these plants and the soil properties in various parts of Doha.
MATERIALS AND METHODS
The study location: The main study location as shown in the Fig.
1 was around Doha city. Samples of the plants and soils were collected from
various areas in that location for different types of analyses required. The
field surveys were started in September 2001 and continued throughout 2002 till
2004. The details of these trips were described by Yasseen
and Abu-Al-Basal (2010). The morphological characteristics of the plant
species covered in this study were determined.
Analysis of soils and plants: Methods of analysis of plants and soils
were described and followed by many authors (Abdel-Bari et
al., 2007; Yasseen and Al-Thani, 2007; Yasseen
and Abu-Al- Basal, 2008). Soil samples were collected from the root zone
of the plants studied and transported to the laboratory. The physical and chemical
properties of soil including water content, soil texture, pH of soil extract,
ECe, mineral content and the field capacity (FC) were studied. The concentration
of major elements (potassium, K+; calcium, Ca2+ and magnesium,
Mg2+) and, sodium, Na+ and chloride, Cl¯ in the water
soil extracts were determined according to the method described by Chapman
and Pratt (1961). Also, trace elements namely, Fe, Cu, Zn, Co, Ni, Cr and
Cd were determined in the water soil extracts and plants using an Atomic Absorption
Spectrophotometer (Model Analyst 700, Perkin Elmer) (Yasseen
and Abu-Al-Basal, 2010). Measurements of the chemical composition were done
on the shoots of plants. The measurements of ionic composition were done according
to the methods of Chapman and Pratt (1961). Proline was
determined according to the method described previously (Bates
et al., 1973). Total Soluble Sugar (TSS) and Total Soluble Nitrogen
(TSN) were determined according to the method described by Alhadi
et al. (1999).
||A map of Qatar showing the study location (It was provided
by the Environmental Studies Centre, Qatar University)
Photosynthetic pigments (chlorophylls a and b as well as carotenoids) were
determined according to the procedure described and used by many authors (Metzner
et al., 1965; Abdel-Bari et al., 2007).
Climatic data: An overall climatic data were extracted from Doha airport
for the last 17 years (Abulfatih et al., 2001).
Description of plants: These plants are found at the coastline from
0 to 500 m from the sea water front to landward and extend to a few kilometers
beyond especially for Ochradenus baccatus. Aeluropus lagopoides
(L.) Trin. ex Thw., Enum. Pl. Zeyl: 374 (1864) Syn. Dactylis lagopoides
L., Mant. 1:33 (1767). Shirraib/Iqrish/Ikrish (Ar.).
This plant is prostrate trailing perennial rigid grass giving off upright short culms up to 15 cm high terminating in inflorescences. Leaves linear; lanceolate 4x0.2 cm, small blades ending in sharp rigid points. Ligules hairy,. Inflorescences 1-3 cm long with small congested and overlapping spikelets. short spicate-sub-capitate broadly pyramidal-sub-orbicular. Caryopsis minute.
The genus Sporobolus is represented by two species in the flora of Qatar. However, only one species is found in our survey; Sporobolus spicatus (Vahl) Kunth, Rev. Gram.1:67 (1829). Syn. Agrostis spicatus Vahl, Symb. Bot. 1 : 9 (1790). Sukham (Ar.).
This plant is very common grass and pale yellow-green short tufted perennial stoloniferous grass. Basal growth arising from the branched stolons is leafy rigid spiky and pungent leaf-blades. Inflorescence narrow spike, 6 cm longx 0.3 cm. Spikelets awnless, 1-flowered. Glumes unequal. Caryopsis ellipsoidal. Flowers throughout the year where moisture is available in cultivated and arable lands, in sewage disposal localities, near residential areas, etc.
Ochradenus baccatus Delile, Descr. Egypte, Hist. Nat. 63 (1814). Kardi
(Ar.). It is densely branched bush appearing dome-shaped with long green±leafless
branches; crown not exceeding two m spread and up to 1-1.5 m high. Plant dioecious,
very rarely monoecious. Inflorescences simple spikes (rarely pedicellated) of
small yellow flowers; male flowers yellow, at anthesis producing large amount
of pollen attracting flies, bees and various other insects feeding on the pollen;
female flowers producing white oval berries about 1 cm long with black seeds
on±sweetish pulp always eaten by birds. It is common in Doha in disturbed
areas. Widespread on University of Qatar grounds, rare in rodats and usually
occurs under Acacia trees on fine to stony-sandy soils., It has been
reported (Wolfe and Shmida, 1995, 1997)
that the male plants representing 35% of this species, whereas 65% were inconsistent
males bearing staminate and pistillate flowers on the same plant (i.e. unisexual,
monoecious) (Abdul-Bari et al., 2007).
Tetraena qatarense (Hadidi) Beier and Thulin. Pl. syst. Evol. 240 (1-4):
36 (2003), (previously known as Zygophyllum qatarense): Hadidi in Boul.
Webb. 32. 2:394 (1978) (http://www.theplantlist.org/tpl/record/kew-2469698),
Shrublet, perennial, fleshy, 40-60 cm high, Branches ascending, purple when
young, then changing into woody, pubscent. Leaves succulent, usually simple,
rarely bifoliate (where moisture is available), petiolate; petioles terete,
It is found on rocky and sandy grounds and is widespread in all disturbed areas
including the coastline and can be found in many locations around the country
(Abdel-Bari et al., 2007). Inflorescences solitary
on short peduncles. Flowers slender, pale yellow. Fruit elongated pale berries
and splitting longitudinally. It flowers during March - April.
Climate and soil characteristics: The climatic data of Doha city that
have been obtained from Doha airport for the last 17 years have given clear
evidence that the environment of Qatar is an arid one (Abulfatih
et al., 2001). For example, the average annual rainfall is 81 mm,
average maximum temperature is 31°C, average minimum temperature is 22°C,
absolute maximum temperature is 47°C, absolute minimum temperature is 1°C,
average morning relative humidity is 71% and average afternoon relative humidity
is 43%. Moreover, the outcomes of the analysis of soil samples collected from
different areas around Doha city confirmed the nature of the harsh environment
of soil. In fact, considerable variations have been found in all parameters
studied including: soil texture, water content, pH of the soil extracts and
ECe; EC of the saturated soil extracts (Table 1).
However, such variations in those parameters were more obvious in ECe;
which accompanied with the variation in Na+ and Cl¯ ions content
in those soils. In fact, the data have shown that the main elements that could
cause salt stress in such soils are Na+ and Cl¯ in addition
to other cations like Ca2+, Mg2+ and K+.
|| Physical and chemical properties of the soil samples collected
from the study location
|aThe number of observations for the soil properties
ranged between 6 to 9. bField Capacity. cECe in allover
the soils around Doha
||The concentrations of soluble trace elements (μg L-1
of soil extract) in the soil samples collected from root zones of the plants
|amg L-1 of soil extract, bThe
number of observations ranged between 6 to 9
|| Shoot chemical composition of the shoot system of the studied
|aThe number of observations was 6
Trace elements were measured in water soil extracts; Fe was found in higher
concentrations followed by Ni, Zn, Cu, Co, Cr and Cd (Table 2).
Plants chemical contents: The chemical constituents (organic and inorganic)
of the shoot system of the plant species are shown in Table 3.
These plants differ in their organic contents under their natural habitats;
O. baccatus accumulated much proline, followed by T. qatarense,
A. lagopoides and the least was found in S. spicatus. T. qatarense,
contained much soluble sugars followed by O. baccatus and S. spicatus
and the least was found in A. lagopoides. Although, little soluble nitrogen
was found in these plants as compared to other plants such as fenugreek (Alhadi
et al., 1999), high concentrations were found in S. spicatus
followed by T. qatarense, A. lagopoides and O. baccatus.
On the other hand, high content of Total Photosynthetic Pigments (TPP) was found
in A. lagopoides followed by O. baccatus and S. spicatus,
while T. qatarense had the lowest concentration among the species
studied. However, chlorophyll a had the main contribution in the order of TPP
contents in these plants. Moreover, the lower concentrations of TPP in T.
qatarense could be a result of the impact of saline soil on plants living
at the coastline, or it could be an artifact of expressing the concentrations
of TPP on fresh weight basis, keeping in mind that this plant has succulent
|| Shoot trace elements content (μg g-1 dry
wt.) of the studied plants
|aThe number of observations was 6
The mineral contents including Na+, Cl¯, K+, Ca2+ and Mg2+ were measured in these plants. The data in Table 3 showed little variation between these plants; however, T. qatarense and S. spicatus accumulated much Na+ and Cl¯ than did A. lagopoides and O. baccatus while these plants had similar content of the major elements. Trace elements were measured in the plants studied and the order of contents was almost as similar as to that in the soil; Fe was found in higher concentrations followed by Ni, Zn, Cu, Co, Cr and Cd (Table 4).
The data of study revealed that wild plants in Doha city-Qatar are exposed
to a number of extreme environmental stresses including drought and salinity
as well as high temperatures during most days of the year. Such conditions could
be a reason behind the great deficit in the soil water content. Also, high levels
of salinity found in such soils could have come from the intrusion of seawater
into the underground waters accompanied with the great evaporation; such conditions
might lead to the emergence of salts on the soil surface. However, great variation
in the ECe values was detected even within the same confined area
of the location studied which can be explained by climatic aridity, rain scarcity
coupled with high evaporation (Abdel-Bari et al., 2007).
These climatic and ecological conditions have put plants under a state of multifaceted
stress. The results of soil analysis have shown that the main elements that
could cause salt stress in such soils are Na+ and Cl¯ in addition
to Ca2+, Mg2+ and K+ (Shonubi
and Okusanya, 2007). Although, the plants under investigation are considered
as xerophytes as can be drawn from the data of soil water content; they might
have also well adapted to saline environments, since they were living in soils
of high salinities. ECe of 45 to 50 dS m-1 was found in soils of
A. lagopoides, S. spicatus was living in a soil
salinity ranged between 107 to 128 dS m-1 while T. qatarense
was living in a wide range salinities from 12 to 187 dS m-1. However,
O. baccatus proved to be typical xerophyte, since it was never found
in saline soils and survived soil water deficit as low as 4-12 % field capacity.
The contents of trace elements in the water soil extracts and in the plant shoots
indicated clearly that Fe was the main trace element found in the plant tissues.
The ranges of concentrations were acceptable and comparable to those recommended
by many authors for normal plant growth (Chapman and Pratt,
1961). Thus, the trace elements found in the soils of Doha area might not
be involved to any extent to the harsh characteristics of these soils (Milner
and Kochian, 2008).
The chemical contents of the plants revealed that O. baccatus and T.
qatarense showed xerophytic characteristics, not only because of the morphological
characteristics and the harsh environment they live in but also they accumulated
substantial amounts of proline to cope with soil of a severe water shortage
(Aziz et al., 2011). Also, the data suggested
exchanged roles between proline and soluble sugars and/or nitrogen in many physiological
and biochemical roles under osmotic stress conditions (Yasseen
et al., 2006; Abdel-Bari et al., 2007).
This means that in many plant systems, osmoregulation inside plant cells can
be achieved mainly either by proline and/or soluble sugars and in such systems
the origin of proline is from the carbohydrate degradation especially when nitrogen
sources are limited (Kavi Kishor et al., 2005).
Other organic solutes might be involved in the processes of osmoregulation in
wild plants when exposed to osmotic stress (salinity and/or drought) (Rhodes
and Hanson, 1993; Youssef et al., 2003). It
was hypothesized that organic solutes such as glycinebetaine could cause a minimum
amount of perturbation of the macromolecular stability and therefore function,
accumulate in the cytoplasm in order to adapt to low osmotic potential. Thus,
glycinebetaine might play the same role the proline does in achieving osmoregulation
and protecting the protein and membrane systems, in S. spicatus and
A. lagopoides, at least under the conditions of the present experiments
(Khan et al., 1998). This needs further investigation
for all wild plants to see what kind of mechanisms these plants might have to
cope with stress conditions (Abdel-Bari et al., 2007;
Yasseen and Al-Thani, 2007; Yasseen
and Abu-Al-Basal, 2010). On the other hand, much soluble nitrogen was found
in the shoots of S. spicatus as compared to the other plants. Low proline
found in this species might cause imbalance in the process of osmoregulation;
such role might be filled with soluble nitrogen components to achieve the osmoregulation
inside the plant tissues (Khan et al., 1998).
Also, the inconsistency in the photosynthetic pigments content found in these
plants can be explained as the great variations in the salinity levels in the
soils of, S. spicatus (ECe: 107-128 dS m-1), A.
lagopoides of (ECe: 45-50 dS m-1) of T. qatarense
(ECe12-187) and O. baccatus (ECe 7-8 dS m-1).
Moreover, high salt stress of the soils could have great impact on the photosynthetic
pigments in the leaves of these plants (Levitt, 1980; Yasseen,
2001) while carotenoids biosynthesis might have promoted under high salt
stress (Gomez et al., 2003). Considerable variations
also found in the mineral contents of the plants studied; however, it seems
that T. qatarense accumulated much Na+ and Cl¯ than did
the others, as this plant survived high soil salinity level of 187 dS m-1.
However, it appeared that these plants are living under extreme stress conditions
of both salinity and/or aridity (Abdel-Bari et al.,
2007). Thus, further studies are needed to investigate the possible mechanisms
of resistance to those conditions, since such plants might have epidermal bladder
cells or hairs as a possible avoidance mechanism to facilitate the excretion
process of extra toxic ions such as Na+ and Cl-1 (Pollack
and Waisel, 1970; Yasseen and Abu-Al-Basal, 2008).
THREATS, SOLUTIONS AND CONCLUSIONS
Perhaps the importance of such studies could come from the fact that many habitats
are disappearing from many locations in the Gulf region, with the completion
of constructions and urban developments due to the great expansion caused
by the establishment of infrastructure of the extraction and industry of oil
and gas (Richer, 2008; Yasseen and
Abu-Al-Basal, 2008). Such studies were trying to address the threats of
those activities on wild plants and, also urging the decision makers to document
endangered wild plants (Gorsi and Shahzad, 2002; Al-Rawahy
et al., 2003) and to implement plans for restoration of vegetation
(Al-Ansi et al., 2004); to maintain the gene bank
stored in them (Yasseen and Al-Thani, 2007). In fact,
urban development and construction activities that are being established in
Qatar could greatly affect the wildlife (Fig. 2). Ecological
restoration as a conservation strategy is urgently required since the world
became conscious of the extent of degradation in landscape and resources due
to human activities. Therefore, such efforts would be possible (Al-Ansi
et al., 2004) for these plants after the determination of physical
and chemical properties of their soils and the ecophysiological characteristics
(Table 1, 3).
||Changes on the ground as a result of the establishment of
towers and buildings which affected the wildlife in Doha: (a) near Qatar
university, (b) inside Doha city
It is worth emphasizing that some ideas have been suggested that might help
the decision makers in such efforts; in addition to the implementation of restoration
and conservation plans; other measures can be taken including: imposing laws,
creating natural reserves, activate the scientific research (Anish
et al., 2008; Siddique and Bari, 2010; Zaman
et al., 2011) and offering the educational materials to improve the
awareness of people to the conservation of natural habitats (Yasseen
and Al-Thani, 2007; Yasseen and Abu-Al-Basal, 2008,
2010). In fact, biologists might have no clear ideas
about the real importance of wild plants in spite of the significant technical
progress in molecular biology, genetic engineering and biotechnology tools.
Moreover, people are not aware of what these plants might hide of unique genes
that could provide experimental materials for modern molecular studies. Thus,
mankind is clinging to what exist on the Earth surface to survive the current
challenges in solving the problems of food crisis or those that might facing
them in the coming years when the population is doubled with limited water and
The author would like to thank Environmental Studies Center, Qatar University, for the technical assistance. The assistance in the description of plants by Professor Ekhlas Abdel-Bari is appreciated.
Abdel-Bari, E.M., B.T. Yasseen and R.F. Al-Thani, 2007.
Halophytes in the State of Qatar. University of Qatar, Doha, Qatar, ISBN-10: 9992152982, pp: 168
Abulfatih, H.A., E.M. Abdel-Bari, A. Alsubaey and Y.M. Ibrahim, 2001.
Vegetation of Qatar. Scientific and Applied Research Center (SARC), University of Qatar, Doha, Qatar.
Al-Ansi, M.A., E.M. Abdel-Bari, B.T. Yasseen and J.A. Al-Khayat, 2004.
Coastal restoration: Restoration of a coastal vegetation habitat at Ras Raffan industrial city. Final Report, SARC, University of Qatar.
Al-Easa, H.S., A.M. Rizk and E.M. Abdel-Bari, 2003.
Chemical constituents and nutritive values of range plants in Qatar. Scientific and Applied Research Center, University of Qatar, Doha, Qatar.
Alhadi, F.A., B.T. Yasseen and M. Jabr, 1999.
Water stress and gibberellic acid effects on growth of fenugreek plants. Irrig. Sci., 18: 185-190.CrossRef | Direct Link |
Al-Rawahy, S.H., K.S. Al-Dhafri and S.S. Al-Bahlany, 2003.
Germination, growth and drought resistance of native and alien plant species of the genus Prosopis
in the sultanate of oman. Asian J. Plant Sci., 2: 1020-1023.CrossRef | Direct Link |
Anish, N.P., M. Bejoy and M. Dan, 2008.
Conservation using in vitro
progenies of the threatened ginger-Boesenbergia pulcherrima
(Wall.) Kuntze. Int. J. Bot., 4: 93-98.CrossRef | Direct Link |
Aziz, I., B. Gul, S. Gulzar and M.A. Khan, 2011.
Seasonal variations in plant water status of four desert halophytes from semi-arid region of Karachi. Pak. J. Bot., 43: 587-594.Direct Link |
Bates, L.S., R.P. Waldren and I.D. Teare, 1973.
Rapid determination of free proline for water-stress studies. Plant Soil, 39: 205-207.CrossRef | Direct Link |
Boyd, C.N., V.R. Franceschi, S.D.X. Chuong, H. Akhani, O. Kiirats, M. Smith and G.E. Edwards, 2007.
Flowers of Bienertia cycloptera
and Suaeda aralocaspica
) complete the life cycle performing single-cell C4 photosynthesis. Funct. Plant Biol., 34: 268-281.
Chapman, H.D. and P.F. Pratt, 1961.
. Methods of Analysis for Soils, Plants and Water. University of California, Berkely, California, USA
Flowers, T.J., 2004.
Improving crop salt tolerance. J. Exp. Bot., 55: 307-319.CrossRef | Direct Link |
Gomez, P.I., A. Barriga, A.S. Cifuentes and M.A. Gonzalez, 2003.
Effect of salinity on the quantity and quality of carotenoids accumulated by Dunaliella salina
(strain CONC-007) and Dunaliella bardawill
(strain ATCC 30861). Chlorophyta Biol. Res., 36: 185-192.PubMed |
Gorsi, M.S. and R. Shahzad, 2002.
Medicinal uses of plants with particular reference to the people of Dhirkot, Azad Jammu and Kashmir. Asian J. Plant Sci., 1: 222-223.CrossRef | Direct Link |
Guan, B., J. Yu, Z. Lu, W. Japhet, X. Chen and W. Xie, 2010.
Salt tolerance in two Suaeda
species: Seed germination and physiological responses. Asian J. Plant Sci., 9: 194-199.CrossRef | Direct Link |
Kishor, P.B.K., S. Sangam, R.N. Amrutha, P.S. Laxmi amd K.R. Naidu et al
Regulation of proline biosynthesis, degradation, uptake and transport in higher plants: Its implications in plant growth and abiotic stress tolerance. Curr. Sci., 88: 424-438.Direct Link |
Khan, M.A., I.A. Ungar, A.M. Showalter and H.D. Dewald, 1998.
NaCl-induced accumulation of glycinebetaine in four subtropical halophytes from Pakistan. Physiol. Plant., 102: 487-492.CrossRef |
Lara, M.V., D.X. Simon, C.H. Akhani, C.S. Andreo and G.E. Edwards, 2006.
Species having C4 single-cell-type photosynthesis in the chenopodiaceae family evolved a photosynthetic phosphoenolpyruvate carboxylase like that of Kranz-type C4 species. Plant Physiol., 142: 673-684.CrossRef |
Levitt, J., 1980.
Responses of Plants to Environmental Stresses. Water, Radiation, Salt and Other Stresses. Vol. 2, Academic Press, New York
Metzner, H., H. Rau and H. Senger, 1965.
Untersuchungen zur synchronisierbarkeit einzelner pigmentmangel-mutanten von Chlorella
. Planta, 65: 186-194.CrossRef | Direct Link |
Milner, M.J. and L. Kochian, 2008.
Investigating heavy-metal hyperaccumulation using Thlaspi caerulescens
as a model system. Ann. Bot., 102: 3-13.CrossRef |
Mohsenzadeh, S., M.A. Malboobi, K. Razavi and S. Farrahi-Aschtiani, 2006.
Physiological and molecular responses of Aeluropus lagopoides
(Poaceae) to water deficit. Environ. Exp. Bot., 56: 314-322.Direct Link |
Pollack, G. and Y. Waisel, 1970.
. Salt secretion in Aeluropus litoralis
(Willd.) Parl. Ann. Bot., 34: 879-888.Direct Link |
Rhodes, D. and A.D. Hanson, 1993.
Quaternary ammonium and tertiary sulfonium compounds in higher plants. Ann. Rev. Plant Physiol. Plant Mol. Biol., 44: 357-384.CrossRef |
Richer, R., 2008.
. Conservation in Qatar: Impacts of Increasing Industrialization. Center for International and Regional Studies (CIRS). Georgetown University, School of Foreign Service in Qatar.
Rizk, A.M. and G.A. El-Ghazaly, 1995.
Medicinal and Poisonous Plants of Qatar. Scientific and Applied Research Center. University of Qatar, Doha, Qatar, pp: 306
Sage, R.F., 2002.
photosynthesis in terrestrial plants does not require Kranz anatomy. Trends Plant Sci., 7: 283-285.CrossRef |
Shabana, M.M., Y.W. Mirhom, A.A. Genenah, E.A. Aboutabl and H.A. Amer, 1990.
Study into wild Egyptian plants of potential medicinal activity. Ninth Communication: Hypoglycaemic activity of some selected plants in normal fasting and alloxanised rats. Arch. Exp. Vet. Med., 44: 389-394.Direct Link |
Shonubi, O.O. and O.T. Okusanya, 2007.
The growth and physiological responses of Paspalum vaginatum
S.W. and Paspalum scrobiculatum
Linn. in relation to salinity. Asian J. Plant Sci., 6: 949-956.CrossRef | Direct Link |
Siddique, N.A. and M.A. Bari, 2010.
Plant regeneration from axillary shoot segments drrived callus in Hemidesmus indicus
, (L.) R. Br. (Anantamul) an endangered medicinial in Bangladesh. J. Plant Sci., 5: 61-67.Direct Link |
Wolfe, L.M. and A. Shmida, 1995.
Regulation of gender and flowering behaviour in a sexually dimorphic desert shrub (Ochradenus baccatus
Delile [Resedaceae]). Isr. J. Plant Sci., 43: 325-337.Direct Link |
Wolfe, L.M. and A. Shmida, 1997.
The ecology of sex expression in a gynodioecious Israeli desert shrub (Ochradenus baccatus
). Ecology, 78: 101-110.Direct Link |
Yasseen, B.T., 2001.
Preliminary assessment of the effect of saline water used in irrigation on the growth of the local Barley cultivar (Harma). Qatar Univ. Sci. J., 21: 55-64.Direct Link |
Yasseen, B.T. and M.A. Abu-Al-Basal, 2008.
Ecophysiology of Limonium axillare
and Avicennia marina
from the coastline of Arabian Gulf-Qatar. J. Coast. Conserv., 12: 35-42.CrossRef | Direct Link |
Yasseen, B.T. and M.A. Abu-Al-Basal, 2010.
Ecophysiology of chenopodiaceae at the coastline of Arabian Gulf-Qatar: Possible destruction and prespective conservation. Eur. J. Sci. Res., 39: 90-104.
Yasseen, B.T., M.A. Abu-Al-Basal and F.A. Alhadi, 2010.
An analysis of leaf growth under osmotic stress. J. Plant Sci., 5: 391-401.CrossRef |
Yasseen, B.T., A. Almuhannady, F.R. Al-Marri and H. Al-Hemiary, 2006.
Changes in soluble sugars and proline in seedlings of a local wheat cultivar (Doha) due to the salt stress and temperature. Qatar Univ. Sci. J., 26: 71-82.Direct Link |
Yasseen, B.T. and R.F. Al-Thani, 2007.
Halophytes and associated properties of natural soils in the Doha area, Qatar. Aquat. Ecosyst. Health Manage., 10: 320-326.CrossRef | Direct Link |
Youssef, A.M., R.A. Hassanein, A.A. Hassanein and A.A. Morsy, 2003.
Changes in quaternary ammonium compounds, praline and protein profiles of certain halophytic plants under different habitat conditions Pak. J. Biol. Sci., 6: 867-882.CrossRef | Direct Link |
Zaman, S., S. Padmesh and H. Tawfiq, 2011.
Selected seed pretreatment on germination of Kuwait's native perennial plant species. Int. J. Bot., 7: 108-112.CrossRef | Direct Link |