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Abstract Fishes are one of the most important groups of vertebrates that serve as food for human. They possess a great nutritional, economic, environmental and social values. In addition, fishes provide employment for great numbers of people in the world (Lynch et al., 2016). Also, fish considered as an essential source of proteins available for humans and other animals in the tropic countries. According to the Food and Agriculture Organization (FAO) of the United Nations, fishes represent more than 40% of the protein diet of two-third of the global population. In addition, fishes are one of the most effective ways to provide protein with relatively competing prices, as other animal's proteins are so expensive (Sabri et al., 2009). Egypt has many sources of fishes; the Mediterranean Sea, the Red Sea in addition to the Nile with several lakes and fish farms. Huge loss of production in aquaculture is occurring because of many reasons. Among these reasons, diseases which are the most serious constraints that cause damage to fish production (Assefa and Abunna, 2018). Parasitic diseases considered one of the most important problems facing fish breeding and production at commercial scales (Abdel-Ghaffar et al., 2009). Parasitic diseases have serious impact on the fish as they cause mortality, low growth rate, lower food conversion rates and decreased marketability as well as it may has zoonotic threats to human consumers (Elsheikha and Elshazly, 2008). Infectious and parasitic diseases of fish cultured under controlled conditions are significant factors restrictive the development of fish aquaculture (Bernad et al., 2017). Also, the study of prevalence of parasites in fishes is necessary and important to decrease their effects on fish population to improve the stocks of valuable commercial fisheries in the natural waters and to the possibility of fish acclimatization in new sites or localities (Shul′man, 1961). 15 Rodger (2016) postulated that the management and control of infectious disease are the main hurdles to sustainable finfish aquaculture in many regions. The study of fish parasites is therefore attractive for many parasitologists, since they not only cause injuries or even death to the fish (Davis et al., 1961), but also do some human health problems (Bernad et al., 2017). In Egypt, parasitic diseases represent about 80% of fish disease (Ghoneim et al., 2015). Thus, the contribution to the knowledge of fish parasitic diseases is a prerequisite for the rapid and correct diagnosis of the disease agent of epizootics. Early diagnosis can lead to preventive measure, which is the best way to reduce outbreaks of disease (Bylund et al., 1980). Following this concept, the present study was therefore suggested to survey the parasites infecting fishes in Lake Wadi El- Raiyan and Bahr Youssef in Fayoum Governorate. Area of study 1- Lake Wadi El- Rayan The valley of Wadi El- Rayan is an area of 1,759 square kilometers, 113 square kilometers of which are the dominating water body of the Wadi El-Rayan lakes. It is located about 65 km southwest of Fayoum city and 80 km west of the Nile River. The source of water in this lake is agricultural and municipal drainage from the El Fayoum province. In 1973, Wadi El-Rayan was connected with the agricultural wastewater drainage system of the Fayuom province and received water that exceeded the capacity of Lake Qarun (Mohamed et al., 2015). 2 – Bahr Youssef Bahr Youssef is a canal which connects the Nile River with Fayoum city in Egypt. It is about 92 km southwest of Cairo. El- Fayoum gets its water supply exclusively from Bahr Yusuf, a side branch of the Nile which leaves the river in the area of Assiut and 16 enters Fayoum at the Lahun Gap (Römer, 2017). Bahr Youssef Canal runs from Ibrahimiya canal of the Nile River at Dirout city that cross Assiut, Minya and Beni Suef Governorates, before entering Fayoum (Bream et al., 2017). Bahr Youssef divided into sub-canals among Fayoum and splits into eight channels (Hewison, 2008). El-Fayoum receives fresh water from Bahr Youssef with a share of irrigation water amounts to approximately 2.5 (bcm) yearly (El- Zieny and Effat, 2019). |