Journal of Environmental Treatment Techniques  
2020, Volume 8, Issue 4, Pages: 1589-1593  
J. Environ. Treat. Tech.  
ISSN: 2309-1185  
Journal web link: http://www.jett.dormaj.com  
https://doi.org/10.47277/JETT/1593  
Water Quality Study of Freshwater of Bekaa Valley  
to the Delta at Mediterranean Seawater in the region  
of Lebanon  
Adnan Falah*, Husein Yemendzhiev, Valentin Nenov  
Department of Water Treatment, Faculty of Technical Sciences, Burgas "Prof. Asen Zlatarov" University, Burgas, Republic of Bulgaria  
Received: 06/06/2020  
Accepted: 26/09/2020  
Published: 20/12/2020  
Abstract  
The water quality of fresh water, springs and wells in Bekaa valley, mountain district, a region of Republic of Lebanon in connection/delta  
of Mediterranean sea (basin) is surveyed along the Lebanese north, central and south coast at Tripoli, Jounieh and Saida deltas respectively  
in which, Sannine Aquifer at Bekaa valley, the major groundwater source for the coastal area is in-direct contact with the sea. The thin  
freshwater lens (delta) is being heavily exploited in this area, where a large number of wells exist in the area passing coastal areas of Lebanon.  
Many of those wells are saline and are not suitable for direct domestic use or even for irrigation. This study deals with water quality study,  
general assessment of level of pollution and potential influence on seawater through analysis of Physico-Chemical parameters and selected  
Inorganic substances of water sample collected from south, central and north Lebanese coastal water among with major water natural  
resources at Bekaa valley.  
Keywords: Water Quality, Bekaa Valley, Mediterranean Sea, Lebanon  
1
drainage system of the Bekaa Valley. These formations have  
1
Introduction  
characteristics for good quality water and are mainly exploited as  
domestic water resources via wells or springs [9, 10]. The  
hydrogeological assets of the Bekaa Valley are strongly  
characterized by the surface water system and its relationship with  
the underground aquifers. There are various drainage systems,  
most of which are dried for most of the year and highly influenced  
by snow melting. Two main rivers flow to south of Lebanon  
called Litani river and to the north called Aassi (Oronte) with a  
division path near the Baalbeck area, the historical city in Bekaa  
province in Lebanon [11-13]. This study is carried out though  
analysis of spring/wells of Bekaa valley and Litani river at the  
delta to Mediterranean basin of Lebanon (Figure 1 and 2), the  
landform created by deposition of sediment that is carried by the  
concerned river as the flow leaves its path end and enters slower-  
moving to the seawater of Lebanese coast.  
Water demand has been continuously increasing and at higher  
rates in most parts of the world and Lebanon is no exception.  
Controlling agricultural water demand is extremely important,  
especially in Lebanon, where about 70 % of water demand is for  
the agricultural sector. Lebanon is a multi-morphological country  
including mountains, valleys and plains. The Bekaa Valley is a  
fertile land passage, separating the Mount Lebanon and Anti-  
Lebanon ranges, drained to the North by the Aassi River (or  
Orontes) and to the South by the Litani River. Bekaa extends for  
,167 km and represents 40 % of the national territory.  
Morphological and geological features are the main factors that  
make Lebanon a country with rich and renewable water resources  
compared to other nearby countries [1-7]. Furthermore, about 65  
2
4
%
of Lebanon is covered by karstic rocks and natural water  
resources characterized by springs, caves and sinkholes. These  
aquifers are highly beneficial, nonetheless extremely exposed to  
water contamination due to anthropogenic activities such as  
quarries, waste depositing and sewage. The main water sources in  
the Bekaa Valley come from surface water, springs and  
underground aquifers. The controlling factor of the underground  
water is the combination of geological structures and composition  
8]. The complex structure of the karstic rocks of the Anti-  
Lebanon unit is one of the most important holding deposits of  
water in the region; numerous springs form the important surface  
2 Materials and Methods  
Mediterranean Seawater (basin) at the delta and  
freshwater/well water samples from different locations in  
Lebanon were collected directly from the source with different  
depths equal to 2, 3 and 5 meters and samples stored properly in  
a plastic bottle. Water collected in triplicate meaning three bottles  
for each sample. All samples are collected-in and analysed within  
eight hours of collection, Physico-chemical parameters such as  
[
*
Corresponding author: Adnan Falah, Burgas "Prof. Asen Zlatarov" University, 8010, Y. Yakimov str.1, Burgas, Republic of Bulgaria,  
E-mail: adnan@falahpwp.com  
1589  
Journal of Environmental Treatment Techniques  
2020, Volume 8, Issue 4, Pages: 1589-1593  
pH, temperature (⁰C), electrical conductivity (microsiemens per  
centimetre, μS/cm), dissolved oxygen, total dissolved solids  
adequate volume of water was removed first by pumping to  
ensure that standing water either in the well or in pipes was  
discarded. UV/Vis spectrophotometer with appropriate reagents  
and test Kits from Merck Spectroquant were used to determine  
the concentration of Inorganic substances like calcium,  
magnesium, sodium, potassium, iron, fluoride, nitrate, sulphate  
and phosphate in water at specific wavelength (nm). Mohr  
method was used for chloride concentration. Agents and  
chemicals used for water analysis experiment were of analytical  
grade [14-18]. Sample collection; Sea water samples were  
collected from three different regions in Lebanon along the  
coastal area of Jounieh, Tripoli and Saida (Figure 1), few hundred  
meters away from the shore and from different depths (2, 3 and 5  
m) in fact, average concentrations were calculated and presented.  
Different samples of fresh water were collected from along the  
course of the stream starting from their sources (wells, springs)  
from Bekaa Valley at Mountain Lebanon area (Figure 1 and 2),  
were taken from each area and analysed to match the existing  
information and obtain indication of potential pollution sources  
that might be from primarily sewage, agriculture as well as  
saltwater interruption with the delta [19].  
(
TDS), alkalinity, salinity and hardness measured in ppm were  
analysed using portable device called “Multi Parameters Portable  
Water Quality Monitor "PWQM" Wagtech) that is capable of  
performing all tests listed above.  
3
Results and Discussions  
Figure 1: General map of Lebanon at Mediterranean Basin and study  
areas of Bekaa Valley and coastal water  
The seawater results of samples analysis at the delta for  
Jounieh, Tripoli and Saida coastal line (Figure 1) are shown in  
Tables 1. Upon investigating the tabulated data, it is found that  
Mediterranean basin/seawater at the delta has an average of pH  
equal to 8.90 where electrical conductivity was 63,550 µS/cm.  
Moreover, average total dissolved solids reported at 40,110 ppm  
were salinity found to be 42,228 ppm so that hardness as CaCO  
3
detected at 3,550 ppm where calcium average is 715.00 ppm.  
Other elements were also analyzed in order to have complete  
assessment of water quality especially at the delta in which  
springs and fresh water direct in-contact with the sea. The average  
concentration of magnesium recorded at 1,840 ppm as well as  
concentration of sodium, potassium, chloride and fluoride found  
to be 5,640, 144, 24,900 and 15 ppm respectively. No indication  
of iron concentration seen. Besides, pollution level is also studied,  
and data shows level of sulphate at 2,530 ppm where  
concentration at 8.50 ppm is for nitrate and finally phosphate test  
recorded at average concentration equal to 26.90 ppm. It seems  
the averages for all three coastal line water regions in table 1, are  
similar to each other; this might be due to large area of thin  
freshwater lens at the delta (Figure 3) [20-24]. The pH and  
chloride levels (average) are found to be fairly close to the  
standard values reported in the literature which are 8.90 and  
24,900 ppm respectively. The reported range for calcium levels  
in seawater vary from 350 to 1,500 ppm and based on date  
obtained in table 1 found to be within the average (715.00 ppm).  
The total dissolved solids value is quite greater than the reported  
value 35,000 ppm [13]. The range of salinity in the open ocean is  
about 31,000 to 38,000 ppm while the salinity value obtained for  
Mediterranean basin is 40,110 ppm. The obtained values of  
potassium and magnesium are within the normal range [14]. The  
proportions of inorganic species are within the expected  
allocations for seawater (Figure 4). However, the three coastal  
regions show quite high phosphate values. This is due to the fact  
that the samples have been taken from shallow sea water where  
the potential of having wastewater discharges into the sea is high.  
High rates of organic decay can produce localized saturation of  
Figure 2: General view of Bekaa Valley and coastal line of Lebanon  
The Calibration of this multi-tester was done at the beginning of  
every sampling day using standard calibration solutions for pH  
and conductivity to ensure reliability of the test results and  
quality. The tester was well dipped by distilled water after each  
testing process. The measuring cup was dipped few times with  
each water sample to be tested. Prior to each sampling process,  
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Journal of Environmental Treatment Techniques  
2020, Volume 8, Issue 4, Pages: 1589-1593  
phosphate in seawater. Water carrying pesticides and fertilizers  
from very near to sea agricultural lands can lead to elevated values  
of nitrate concentration as can be seen from the results [25, 26].  
The low dissolved oxygen values obtained in the three regions  
along the Lebanese coast ranging from 5.87 to 6.22 ppm are an  
indication of organic pollution of sea water. This might be due to  
excessive dumping of garbage, waste and sewage into the sea  
especially in the regions close to the shore [17].  
nitrates in high concentration in drinking water is harmful to  
human health. Water hardness is equivalent to the concentration  
of Ca and Mg .  
2+  
2+  
Calcium (mg/l)  
Fluoride (mg/l)  
Iron (mg/l)  
0
%
17%  
%  
0
Table 1: Analysis of Physico-Chemical properties and  
concentrations of selected inorganic substances of water samples  
from three different regions in Lebanon along the coastal area of  
Jounieh, Tripoli and Saida  
70%  
Magnesium  
(mg/l)  
Figure 4: Relative proportions (Average) of dissolved salts in seawater  
It reflects the nature of the geology in the area of the stream.  
Samples with hardness values between 200 and 300 ppm CaCO3  
are considered hard water and have a bitter taste. It could also be  
shown from the results that the well/spring water average has a  
high electrical conductivity value; this quality of water with high  
average of EC could be harmful to plants or other organism [18-  
2
(
5]. Figure 5 illustrate the relative distribution proportions  
average) of dissolved salts in Bekaa Valley well/spring water  
where, Sodium and Chloride have the higher portion of 74% and  
5% respectively. Other extended analysis data are tabulated in  
1
Table 2. Spring water in Bekaa valley is significantly used for  
drinking, in farming, irrigation and industrial activities. The  
Bekaa itself, is Lebanon’s largest province and has the largest area  
of arable land to date. It has a moderate dry and warm climate in  
summers and wet to snowy winters (Mediterranean climate). The  
Bekaa is located about 30 km east of Lebanon’s capital Beirut.  
The Bekaa valley is situated between Mount Lebanon to the west  
and the Anti-Lebanon mountains to the east. It is 120 Km long  
and 16 Km wide on average. Diversely, threats to its water  
supplies would severely affect the economy of the province. The  
Bekaa valley is a huge agricultural land with a fertile soil and low  
population compared to other provinces [19-21]. Most towns and  
villages in the Bekaa Valley have no significant sewer systems  
thus, notable portion of wastewater discharged untreated into a  
nearby valley. Litani river, the important water resource in  
southern Lebanon which is rises in the fertile Bekaa Valley (west  
of Baalbek historical city of Bekaa province) and empties into  
the Mediterranean Sea at north delta of Lebanon. Many towns and  
areas among Litani River had a sewer system installed in the early  
6
5
4
3
2
1
5,000.00  
5,000.00  
5,000.00  
5,000.00  
5,000.00  
5,000.00  
5
,000.00  
-
5,000.00  
Figure 3: Comparison analysis and concentrations of selected physical  
parameters and inorganic substances of water samples from Jounieh  
Left), Tripoli (Middle) and Saida (Right)  
(
1990s, but its waste flows, untreated, into the adjacent Litani  
River. During the summertime, when the river’s flow slows to its  
minimum, the problem becomes more serious due to excess  
amount of waste and backlogs in the sewer system that affect the  
river flows mood. Since many unscrupulous farmers inn towns  
and cities are known to draw water from the river to irrigate their  
summer crops, which they market locally and in Beirut capital.  
The impacts on people’s health as a result of the farmers’ use of  
contaminated irrigation water remain undocumented. However,  
by referring to the obtained results and compare them with the  
reported values in literatures, the potential influence of Bekaa  
valley’s water (fresh, well, springs) to the seawater quality  
became sharper to spot.  
On the other hand, water quality in the Bekaa Inland were  
investigated, samples were taken from both wells and springs in  
the Bekaa region. Groundwater constitutes the major source of  
fresh water in Lebanon. Bekaa Valley relies by 90% on  
groundwater resources for agriculture and domestic use. The  
results shown in Table 2 is assessed. and it is found that chemical  
constituents of the Bekaa spring water values are below the upper  
permissible limits imposed by USA-EPA (Environmental  
protection agency) and WHO (World health organization) for  
drinking water; knowing that the upper permissible limit of  
sulfate in drinking water is 400 mg/l. It should be noted that  
1591  
Journal of Environmental Treatment Techniques  
2020, Volume 8, Issue 4, Pages: 1589-1593  
in the recharge values due to climatic changes or extensive human  
activities or untreated flows, affects the naturally occurring  
equilibrium negatively and that is the case now; greater recharge  
shifts the interface towards the sea whereas any deficit in this  
recharge causes seawater violation into coastal fresh water  
aquifers. Moreover, the quality of seawater at the delta is in  
deterioration state due to lack of treatment from the sources such  
as Litani river and other fresh water entering the seawater. On the  
other hand, drilling a huge number of wells to high depths and  
exploited at high rates is speeding the rate of seawater interference  
and making new paths for seawater flow in fact, seawater  
continue to encroach inland which coincides with areas of high  
population densities. The potential impact from excess wells  
usage in the concerned areas meaning that residents are producing  
the extensive over abstraction of the coastal aquifers mainly  
Sannine aquifer since it is in-direct contact with the sea. Thus, at  
these focused zones, groundwater is no more fresh and the  
situation is thought to become much worse if people continue to  
exploit the groundwater at the same way [26-31].  
Table 2: Analysis of Physico-Chemical properties and average  
concentrations of selected inorganic substances of water samples  
from Bekaa Valley Well/Spring water that in contact with Sea at  
the delta in Lebanon (Mediterranean Basin)  
4
Conclusions  
Based on data compared in Table 1 and 2 with and standards  
in literatures, it seems that groundwater quality of a different parts  
of the Bekaa Valley is getting poor to very poor-quality  
characteristics. Water management and further monitoring are  
highly required to treat contaminated water and reduce sources of  
pollution. Groundwater over the studied areas are not protected  
and more strategies needed to inhibit loss. Groundwater managing  
laws and regulations exist, however they are not strictly enforced.  
However, Water quality for drinking and irrigation purposes need  
to be managed based on standards regulations. Continuous  
monitoring of groundwater as well as sea water at the delta is  
required especially for the areas of agricultural, for constructing  
better management plans. This study might add and providing  
useful data and awareness for future observations and better  
managements [32].  
Calcium (mg/l)  
1
%
%  
1
5%  
Fluoride (mg/l)  
Iron (mg/l)  
0
%
7
4%  
Magnesium  
(mg/l)  
Ethical issue  
Authors are aware of, and comply with, best practice in  
publication ethics specifically with regard to authorship  
Figure 5: Relative distribution proportions (Average) of dissolved salts  
in Bekaa Valley well/spring water  
(
avoidance of guest authorship), dual submission, manipulation  
of figures, competing interests and compliance with policies on  
research ethics. Authors adhere to publication requirements that  
submitted work is original and has not been published elsewhere  
in any language.  
The Lebanese coastal zone is the most perceptive zone in the  
country, it is expands over 210 km in length in which industrial,  
commercial, entertainments, beeches, resorts and financial  
activities along with major Lebanese cities are generally  
concentrated; mixing salinity zone or the fresh-salt water that is  
in-direct contact with seawater from rivers and wells especially  
from Bekaa valley, has exceeded the limit which requires more  
attention to sustain desirable quality of water. Though, coastal  
aquifers, a natural gradient still exists towards the coast and  
groundwater discharges from areas of higher groundwater levels  
into the sea. This naturally occurring movement of fresh water in  
fact, prevents saltwater from entering freshwater coastal aquifers.  
The flow of saltwater inland, or horizontal seawater  
encroachment, is limited to coastal areas. As we go further inland,  
the freshwater head is higher thus, it is able to equalize the  
pressure from the saltwater, preventing saltwater interference so  
that a saline wedge below the fresh water is formed and the  
density is high enough to prevent substantial mixing and thus a  
natural hydrostatic equilibrium is developed in fact, any change  
Competing interests  
The authors declare that there is no conflict of interest that  
would prejudice the impartiality of this scientific work.  
Authors’ contribution  
All authors of this study have a complete contribution for data  
collection, data analyses and manuscript writing.  
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