Authors
1 Animal Health Research Institute, Assiut Regional Lab.
2 Dept. of Parasitology, Animal Health Research Institute, Assiut Lab.
Abstract
Keywords
CRYPTOSPORIDIUM AND OTHER ZOONOTIC PARASITES IN OREOCHROMIS NILOTICUS IN ASSIUT GOVERNORATE
M.A.M. AMMAR and M.I. ARAFA
Animal Health Research Institute, Assiut Regional Lab.
Email: mohsenpara22@yahoo.com
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ABSTRACT
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Received at: 30/9/2013
Accepted: 25/11/2013 |
This study was carried out on 120 Oreochromis niloticus fish (60 wild and 60 cultured). The fish were randomly collected, from different areas of Assiut Governorate as well as from some fish farms. They were used to investigate the prevalence of Cryptosporidium and other zoonotic parasites in O. niloticus. Examination of gills, muscles and the contents of the gastrointestinal tract revealed highest parasitic infestation rate (80 %) in wild compared to (55 %) in cultured O. niloticus. The prevalence of the isolated parasites in wild and cultured O. niloticus was as follows: Cryptosporidium spp. 15.0 % and 23.3% respectively; Acanthocephela (Acanthocentius tilapae) 8.3 % and 9.2% respectively; microscopic encysted metacercariae 88.3% and 26.7 % respectively while macroscopic encysted metacercariae detected only in wild O. niloticus 40%. Killing factors (temperatures, solutions and processing methods) were studied on encysted metacercariae (EMC) in O. niloticus killing criteria followed the movability index (MI) from 1.000 within 24 hours. Muscle pieces containing viable EMC were incubated in different concentrations of NaCl, acetic acid or commercial vinegar at room temperature. The MI was ≤1 (killing effect) within 1, 2 hours for 30% and 20% of NaCl respectively and 1, 6 and12 hours for 5, 2.5 and 1.25%of acetic acid, respectively while commercial vinegar has MI ≥1 (no killing effect) at 5%.Storage of O. niloticus at (-10 ̊C) resulted in killing the EMC after 12 hours of storage while storage at 5 ˚C for 24 hours has no killing effect. Dry salting of O. niloticus could kill the EMC within one hour of salt contact, while marination in 5 % acetic acid for one minute resulted in eradication of EMC after 2 hours of treatment with barely detected acetic acid odor and significant reduction in muscle pH (P < 0.05.).
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Keywords: Cryptosporidium, zoonotic parasites, fish, Killing factors, processing methods, encysted metacercariae (EMC).
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INTRODUCTION
Fish meat demand as human food is increasing especially in the developing countries where people income is low. World fish production has grown tremendously in the second half of the 20th century (Pillay, 1990). Egyptian per capita fish consumption is more than doubled from below 7kg in 1990 to over 14 kg in 2002, (Suloma and Ogata, 2006). Tilapia is the predominant aqua-cultured finfish in Egypt and represented 14.5% of the coounty's total fish landing and is a componant of traditional Egyptian diet (Green et al., 2002).
Salted, salt fulminated, smoked and fried fish are the favorite traditional fish dishes on the Egyptian people. The effect of some traditional processing methods on EMC is remained uncertain. Eating the EMC in row or under processed fish constitute a zoontic risk (Huss et al., 2003).
A multitude of parasites have been reported in fish, but only a few species are capable of infecting human (Adams et al., 1997). Recent reports suggest that fishes act as a source of serious human parasitic infectious diseases (EFSA, 2010). Fish borne parasites infecting human results from food habits of the people by consuming raw, partially cooked, slightly salted or smoked fish (Abd El-Maksoud, 1992). Members of the genus Cryptosporidium are parasites of the intestinal tracts of fishes, reptiles, birds, and mammals. People may be infected by consuming contaminated water or food. Cryptosporidiosis is an emerging disease in both wild and farmed fish in numerous countries worldwide (Sitja-Bobadilla et al., 2005). Relatively little is known about the prevalence and geographic distribution of Cryptosporidium isolates that infect fish in Egypt. Heat inactivation of parasites proved effective for eliminating the risk of parasitosis but trematodes possessed a higher heat resistance (Hus et al., 2003). So far fish processors need alternative easy, fast, cheap and effective measures for eradication of EMC. However the appropriate inactivation technologies in freshwater fish are not well established. Therefore the present study aimed to:
- Document the prevalence of Cryptosporidium and other zoonotic parasites in one of the most common edible fishes (Oreochromisniloticus) that might cause public health problems, if these fishes were eaten improperly cooked.
- Investigate the effect of some killing factors: temperatures, solutions and processing methods on encysted metacercariae (EMC).
MATERIAL and METHODS
1- Samples:
A total number of 120 specimens of O. niloticus (60 farmed fish & 60 wild fish) were randomly collected from different localities of the River Nileand from some fish farms at Assiut Governorate.
2- Parasitological examination:
(A) Macroscopic examination:
Macroscopic examination was carried out either by naked eye or by the magnifying hand lens (2 X and 4X) for detection of encysted metacercariae (EMC) in musculature and gills (Mahdy et al., 1995).
(B) Microscopic examination:
Muscles were screened for the presence of EMC by compression method in which snips were taken from muscles of each part of fish body (head, trunk and tail). Each piece was compressed between two microscopic glass slides and examined microscopically for the presence of EMC (Sayasone et al., 2007).
Metacercariae were identified to genus level based on the morphological details, their dimensions, shape of cysts, site of infection, and shape and contents of excretory bladder under light microscopy (Amer, 1996; Sohn et al., 2005 and Elsheikha and Elshazly, 2008).
The stomachs and intestines were dissected and placed in separate Petri dishes with physiological saline solution, and washed by saline solution. Mucosal scrapings were collected and centrifuged for concentration of oocysts (Waldman et al., 1986). Smears were done from the sediment and stained by a modified Zeil- Neolsen acid-fast (Henriksen and Pohlenz, 1981).
The collected Acanthocephela were first washed in saline solution, refrigerated in cold water for 12 hours to protrude its proboscis, were relaxed and fixed in AFA (Alcohol formalin acetic acid), dehydrated and mounted (Pritchard and Kruse, 1982).
3- Studying the effect of sodium chloride (NaCl), acetic acid and vinegar on encysted metacercariae in O. niloticus muscle pieces:
Ten pieces (about 1 cm3 each) of heavily infected fish muscles containing active encysted metacercariaewere soaked in a 20ml solution of (40,20,10,5,2.5, 1.25 and 0.3 %) concentrations of acetic acid, (40,20,10,5,2.5, 1.25 and 0.3 %) Na Cl or (5, 2.5, 1.25 and 0.3 %) vinegar, individually in a plastic plate. Infected fish muscle pieces containing active encysted metacercariae were soaked in 20ml distilled water as a control. For each concentration and control the muscle pieces were examined at 0,1,2, 4,6, 12, 18 and 24h of soaking and transferred to another plate contains 20ml of 0.89% Na Cl and examined for metacercariae movement using light microscope. The assessment of the effect of treatment was done using the movability index (MI) recommended by (Prawang, 2001) and the killing criterion described by (Wongsawad et al., 2005). Since MI value ≤ 1.0 within 24h refers to the death while MI > 1.0 refers to the survival of the metacercariae.
4- Studying the effect of storage temperature or different processing methods onEMC:
Freshly caught O. niloticus (50 -70gm each) were examined for presence of active EMC. A sufficient number of highly infected fish were eviscerated, washed and divided into the following groups:
GA were put in tightly closed plastic bags and subdivided into GA1 (were refrigerated at 5˚C) and GA2 (were frozen at -10 ˚C). GB were soaked in acetic acid 5% for one minute at room temerature. GC were dry salted at room temperature using NaCl (NaCl/fish =3/10gm). GD was control group. The assessment of the effect of different factors on EMC was done by reporting the MI at 0, 1, 2, 4, 6, 12, 18 and 24h according to (Prawang, 2001) and (Wongswad, 2005).
(A)- pH measurement: :( Sallam, 2007)
Ten grams of each sample were blended with 20 ml distilled water in a blender for 30 s and pH value of fish homogenate was measured by a digital pH-meter (Gallenhamp No.101284) standardized at pH 4 and 7.
(B)- Sensory assessment: (Sallam, 2007)
Fish samples soaked in acetic acid for one minute as well as control samples were separately wrapped with aluminum foil, cooked in steaming pot until the core temperature of each sample reached 70 ċ. stick water was drained and allowed to cool to room temperature (25-28 ċ).The acceptability of cooked samples was evaluated by 5 semi-trained panelists.
Panelists were asked to evaluate the overall acceptability with regard to appearance, odour intensity, flavour and aftertaste, tenderness, juiciness, off-odour, and off-flavour according eight-point hedonic scoring scale. Samples receiving overall scores of more than 4 were considered acceptable, while a score between 3 and 4 was considered the borderline of acceptability. The packaged SPSS program for windows version 12.0.1 was used for statistical analysis according to (SPSS 2007). Data were expressed as mean ± standard error (SE). Differences between groups were determined by means of a Student "t"-test. Significance level was set at P < 0.05.
RESULTS
Table 1: Prevalence of different zoonotic parasites in examined fish.
Source of fish |
Ex. fish |
Inf. fish |
%
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Cryptosporidium
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Acanthocephalus
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Encysted metacercariae |
|||||||
Macroscopic m. (Gills)
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Microscopic m. (Muscles)
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Total infection |
|||||||||||
Inf. No
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% |
Inf. No
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% |
Inf. No
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%
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Inf. No |
% |
Inf. No. |
% |
||||
Farmed Fish |
60 |
33 |
55.0 |
14 |
23.3 |
6 |
10.0 |
0 |
0 |
16 |
26.7 |
16 |
26.7 |
Wild fish |
60 |
48 |
80.0 |
9 |
15.0 |
5 |
8.3 |
24 |
40.0 |
53 |
88.3 |
59 |
98.3 |
Total |
120 |
81 |
67.5 |
23 |
19.2 |
11 |
9.2 |
24 |
20.0 |
69 |
57.5 |
75 |
62.5 |
Table 2: Prevalence of different metacercariae detected in examined fish.
Source of fish |
Infected Fishes |
|||||||||||
Total Macroscopic meta. |
Total Microscopic meta. |
Mixed infection |
Single Macroscopic meta . |
Single Microscopic meta. |
Total infection |
|||||||
infected No. |
% |
infected No. |
% |
infected No. |
% |
infected No. |
% |
infected No. |
% |
infected No. |
% |
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Farmed Fish |
0 |
0 |
16 |
26.7 |
0 |
0 |
0 |
0 |
16 |
26.7 |
16 |
26.7 |
Wild fish |
24 |
40.0 |
53 |
88.3 |
18 |
30.0 |
6 |
10.0 |
35 |
58.3 |
59 |
98.3 |
Total |
24 |
20.0 |
69 |
57.5 |
18 |
15.0 |
6 |
5.0 |
51 |
42.5 |
75 |
62.5 |
Table 3: Prevalence of different species of metacercariae in examined fish.
Types of metacercariae |
Farmed fish |
Wild fish |
Total |
|||
N0. of Inf. fish |
% |
N0. of Inf. fish |
% |
N0. of Inf. fish |
% |
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Microscopic m: 1-Prohemistomum spp.m 2- Haplorchis spp.m 3- Diplostomum spp.m
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16 9 0 7
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26.7 15.0 0 11.7
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53 33 3 17
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88.3 55.0 5.0 28.3
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69 42 3 24
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57.5 35.0 2.5 20.0
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Macroscopic m: 1-Clinostomum phalacrocoracis 2-Clinostomum tilapiae |
0 0 0 |
0 0 0 |
24 23 1 |
40.0 38.3 1.7 |
24 23 1 |
20.0 19.2 0.8 |
Table 4: Effect of chemicals on movability index (MI) of ECM.
Parameter |
Acetic acid |
Sodium chloride |
Vinegar |
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Conc |
Duration in hours |
Conc. |
Duration in hours |
Conc |
Duration in hours |
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MI≤1 |
5% |
1 |
30% |
1 |
- |
- |
2.5% |
6 |
20% |
2 |
- |
- |
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1.25% |
12 |
- |
- |
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|
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MI≥1 |
0.6% |
24 |
10% |
24 |
5% |
24 |
0.3% |
24 |
5% |
24 |
2.5% |
24 |
Table 5: Effect of processing or storage temperature on movability index (MI) of EMC.
MI≤1 |
MI≥1 |
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Processing |
Duration in hours |
processing |
Duration in hours |
Soaking in acetic acid 5% for 30s |
2 hours after treatment |
Soaking in acetic acid 2% for 60s |
24 hour after treatment |
Dry salting |
1 |
Storage at 5ć |
24 |
Storage at -10ć |
12 |
Table 6: Effect of processing O.nioticus with acetic acid on pH and sensory quality.
Parameters. |
pH |
Sensory evacuations |
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Odour intensity |
Juicen-ess |
Tenderness |
Appearance |
Unpleasant odour |
Overall acceptability |
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Mean Treat. |
5.07±0.22 |
5.33±0.33. |
7.67±0.33 |
7.33±0.33 |
7.00±0.00 |
5.00±0.00 |
31.67±0.22 |
Slight intense |
Extreme juicy |
Very tender |
Moderate |
Barely detected |
Acceptable |
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Mean. Cont. |
6.03±0.12 |
6.67±0.33 |
7.33±0.33 |
5.67±0.33 |
7.33±0.33 |
6.00±0.00 |
32.67±0.12 |
Very intense |
Very juicy |
Moderate tender |
Moderate |
Not detected |
Acceptable |
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P-value |
0.027 |
0.092 |
0.211 |
0.065 |
0.211 |
0.0005 |
0.113 |
DISCUSSION
Parasitic fauna of fishes respond strongly to alterations in the physical and chemical characteristics of aquatic environment and modifications in the physiological and biological conditions of hosts (Ferrari- Hoeinghaus et al., 2006).
The results of the present study showed that, parasite community of wildandfarmed O. niloticus consisted of, one protozoon (Cryptosporidium spp. 19.2%), one Acanthocephalan (Acanthocephalus spp 9.2%) and five trematode metacercariae (Prohemistomum spp. 35.0%, Diplostomum spp. 20.0%, Haplorchis spp. 2.5%, Clinostomum phalacrocoracis 19.2% and C. tilapiae 0.8%).
The overall prevalence of examined fish was 67.5 %, highest infestation rate was detected in wild O. niloticus 80 % compared to 55 % in farmed one (table 1). Contrary to these results were recorded by (Eissa, et al., 1996) who reported that the infection rate in farmed and wild fish in Sharkia Governorate
was 67.33% and 42.33% respectively. Also Ibrahim (2012) recorded that the infection rate in farmed fish was 63.51% and in wild fish was 44.37% in Ismailia Governorate.
The difference of percentage may be attributed to the sanitary condition of the place, the location of the river from living place, number and class of people visiting the river and their purpose, biological pollution and snails propagation which act as intermediate hosts to complete the life cycle of some trematodes. In addition to good environmental conditions carried out by fish farmers in the study area.
Skinner (1982) mentioned that chronic exposure to pollutants or any environmental stress which lead to immuno-suppression through the release of corticosteroids make the fish more susceptible to any pathogenic organisms. This is considered the main factor responsible for the high rates of parasitic diseases in fish.
Examination of MZN stained intestinal contents smears in the present study revealed that 23 fish (19.2%) were positive for Cryptosporidium sp. The infection rate in farmed fish was 23.3% while in wild fish it was 15.0 % (table1). Gastric and intestinal cryptosporidiosis has been previously identified in 14 species of marine and freshwater fish (Alvarez-Pellitero et al., 2004 and Xiao et al., 2004). Hefnawy (1989) detected Cryptosporidium in 30 % of Tilapia in Assiut. Al- Taee (2008) detected it in 28.97 % in examined fish from Mosul. Abd-Allah (2009) detected C. parvum oocysts with infection rate of 13.75% in crayfish at Zagazig. Also Mahmood (2012) detected it in 16.9 % of carp fish in Iraq. The variation in the rate of infections may be due to the genus and numbers of fish, time of samples collection and examination, the rate of contaminated water, stress exposed in addition to the methods used for the diagnosis.
On the other hand, highest infection rate in farmed fish may be related to food supply in addition to over crowding which leads to the high and quick spread of infectious diseases in farmed fish. Additionally, fish farming in rural areas is always integrated with poultry production and this might have contributed to the parasitic infection which some species may cross infect between fish and domestic poultry (Aiello and Mays 1998).
The appearance of detected Cryptosporidium oocysts after staining with modified Zeihl- Neelsen was bright red spherical oocysts with a diameter of 5.2 x 4.4 μm, and that agree with the description by (Xiao et al., 2004 and O' Donghue, 2005).
Cryptosporidium lacks species host specificity (Xiao et al., 2004). Therefore, domestic and wild species of animals may be reservoirs of infection for susceptible human individuals, whether they are immunodeficient or immunologically competent. Accordingly, the infected fish play a role as reservoirs and can shed massive amount of infective oocysts to the aquatic environments, so this pathogen has been isolated worldwide from rivers, lakes and other sources of water (Baruš et al., 2002 and O' Donghue, 2005).
On the other hand adult worms of Acanthocephela were detected in 9.2% of examined fish, their infection rate in farmed and wild fish was 10.0 % and 8.3 % respectively (table 1). This result some what agrees with that of Eissa et al. (1996) and Abdel-Mawla and El-Ekiaby (2012) in both farmed and wild Tilapia, but high prevalence was detected in Tilapia by El- Naffar et al. (1983) 43.2% and Eissa et al. (2010) 46.9 %. Although, they disagreed with the prevalence, all agreed that O. niloticus is the only species of fish infested with Acanthocephala spp. through feeding on fresh water crustacean (Duijn, 1973). Ramadan (1991), mentioned that the kind of food is a fairly factor in determining the type of helminth parasites which can be found in a fish. Martin et al. (2009) reported that, high stocking densities favors increased parasite populations.
Natural infestation of man with Acanthocephala is rare, but possible where eating habits are unclean. In some cases they can cause great pain to the host if the proboscis completely perforates the gut wall. Subsequent natural infections with Acanthocephala have since been reported, (Tada et al., 1983). Eight species have been isolated from humans to date (Haustein et al., 2009).
Concerning to the prevalence of encysted metacercariae in the present work, total infection rate was 63.3%. They were differentiated into microscopic encysted metacercariae 57.5% and macroscopic 20.0 % (table 1). These findings are nearly similar to those given by Arafa et al. (2005) 42.86% Abd-El- Rahman (2005) 45% and Abd-Allah (2009) 32.2 %. However, higher prevalence war recorded by Khattab (1990) 87.06 % and Taher (2009) 84.75%. Taher, (2009) suggested that such variation in prevalence may be related to the difference in the habitat, food supply, abundance of both aquatic snails (the intermediate host), and the aquatic piscivorous birds, which play the main role to complete the life cycle of some digenetic trematodes.
The highest infection rate with microscopic metacercariae was detected in wild fish(88.3%), while macroscopic metacercariae were not detected in farmed fish (table1). The present authors suggest that such results may be related to the wide area of surface water of River Nile and their richness with aquatic snails (the intermediate host) and presence of aquatic birds around it is considered the most important points which lead to increase the infestation rate in wild fish.
Microscopic metacercariae detected in the present work were differentiated into: Prohemistomum sp. (35.0%), Haplorchis sp. and (2.5%) Diplostomum sp. (20.0%), while macroscopic metacercariae detected in the present work were differentiated into: Clinostomum phalacrocoracis (19.2%) and Clinostomum tilapiae (0.8%).
Most of these metacercariae were detected previously by El- Shahawi (1983), El-Naffar, and El-Shahawi (1986), Hussein (2007) and Taher, (2009).
Trematode metacercariae are considered as one of the most common parasites infesting fish; some of these parasites may have zoonotic importance (Hernandez et al., 1998). Yellow grub (Clinostomum metacercariae) causing Halzoun like disease, while Prohemistomum vivax may causing death for human being (Nasr, 1941 and Williams and Jones, 1976).
The majority of human infections with trematode result from the consumption of raw or lightly cooked freshwater fish or shellfish containing viable metacercariae. Depending on the parasite species, these infections may occur in the liver, lungs, small intestine and occasionally brain or other tissues producing symptoms ranging in severity from mild to debilitating and life-threaten (Amin, 2005). In surveys a true picture of the prevalence in humans with these parasites is difficult to attain because of the similarity of their eggs of many species(Healy, 1970).
Encysted metacercaria (EMC) develop in O. niloticus as intermediate host. The effects of aberrant physico-chemical microenvironment (e.g. salt, vinegar and acetic acid) concentrations for different exposure times on EMC were studied. The in vitro investigation showed that the tested EMC were killed within 1, 6 and 12 hour of incubation in 5, 2.5, and1.25% acetic acid, respectively (Table 4). Acetic acid is generally recognized as safe by The United States Food and Drug Administration (FDA). Most research on individual or combined effect of acetic acid has focused on surface contamination of fish and fresh meat surface (Ahmed 1999). However, few studies directed toward the wormcidal effect of acetic acid. With The Far East Stellantchasmus falcatus EMC, Wongsawad et al. (2005) found that the metacercariae were killed in acetic acid at concentration of 5 or 10% within 12 and 6 hours, respectively. Sukontason et al. (1998) stated that 5% acetic acid has no killing effect on trematode EMC within 3hours.
Vinegar is one of the oldest fermented food items enjoyed by man and widely used in food industry. In our study, commercial vinegar (5% Conc.) has no killing effect on ECM (MI≥1 within 24hour), (Table 4). Murrell, (2002) reported that commercial vinegar (4% Conc.) has no killing effect on O. viverrini EMC within one hour.
The results summarized in Table 4 revealed that common salt (NaCl) could kill the EMC (MI≤1) at Conc. 30, 20% within 1and 2 hours, respectively. Lower Conc. (10 and 5%) have MI≥1 within 24 hour (no killing effect). The sodium chloride micro environment effect on ECM was investigated by other researchers. Wiwanitkit et al. (2002) stated that degeneration of all Haplorchinae spp. metacercariae took approximately 3 hours by marination in 5% sodium chloride. With The Far East indigenous Stellantchasmus flacatus metacercariae, Wongswad et al. (2005) found that the worms were killed in NaCl 20, 30, 40 % solutions within 12, 6 and 2 hours, respectively.
Fish processors are in need of methods to eliminate parasites in fish rather than cooking. In our study, different storage and processing methods were evaluated as control measures of the ECM in O. niloticus within 24 hour. Chilling and freezing are the normally employed methods for fish preservation. Cold storage of O. niloticus at 5 ̊C for 24 hours dose not affect the viability of ECM (MI ≥1within 24h), (Table5).
Youssef et al. (1993) found that chilling muscle pieces of fish at 4ċfor 24hour has no killing effect on trematode EMC. Abdalah et al. (2009) stated that it took 11-15 days of storage at 5˚ċ to achieve complete loss of viability of four different trematode ECM while Wiwanitkit et al. (2002) found that refrigeration of freshwater fish for approximately 5hours resulted in degeneration of all Haploirchinae spp.
By freezing, killing of parasites depends on several factors. The temperature of freezing process, length of time that fish is held frozen and type of parasite appear to be the most important, FDA (2001). In the present study storage of O. niloticus at -10 ̊C for 12 hours resulted in complete loss of ECM viability (Table5).
With the same fish species, Abdallah et al. (2009) mentioned that it took longer time (16h of storage at -10 ̊C) to gain complete loss of Dilpostomatidae ECM viability. A shorter time (5h) was enough to degenerate all Haplorchinae spp. ECM in freshwater fish, Wiwanitkit et al. (2002).
Marinating is the process of soaking foods in a seasoned, often acidic, liquids with or without cooking. The aim of marinating is not only to inhibit the action of bacteria but also tenderize the connective tissue, EFSA (2010). In this study the present authors investigated the effect of soaking of O. niloticus in acetic acid on viability of EMC. The data summarized in (Table5), revealed that it took two hours after soaking of fish in acetic acid for one minute to gain MI≤1 (killing effect). In general, little was known about the effect of acid on fish trematodes, mainly ECM., Zviagina and Beer (1997) found that 3% acetic acid was minimally effective in suppressing the viability of O. felineus ECM while 6% concentration was about 6 times higher. Wiwanitkit et al. (2002) reported that marinating freshwater fish for approximately 3 hours was enough to degenerate Haplorchinaespp. EMC.
Dry salting was the most effective processing mean in our study. It could kill the ECM in O. niloticus muscles within one hour, (Table, 5). Parasites vary in their response to common salt, research studies indicated that parasites can be eliminated at high salt concentrations for a short period, some of them can also be killed at low salt content. That will depend on fat content, temperature, amount of salt, salt composition, et. (Mol and Ozden 2004).
Fan (1998) stated that keeping the freshwater fish in heavy salt (fish/salt=10gm/3gm) may not be effective in the prevention of clonorchiasis. Sukontasoy et al. (1998) found that 10 % NaCl has no killing effect on trematode ECM in fish within 3 hours. Murrell (2002) reported that dry salting was lethal for anisakids within ten minutes of direct contact.
Knowledge about the pH of fish flesh may give valuable information about its condition. The pH value of seafood varies from 5.8-7.2 depending on struggling at time of harvesting but normal variation is of pH 5.8-6.5 Ali (2011). The present data summarized in Table 6 verify that acetic acid soaked fish had a significant lower pH (p‹0.05) values compared to control. Lowering the pH by acid application is the chief application in foods, (Ahmed, 1999).
Sensory assessment has always played a key role in quality and freshness evaluation in fish industry. In our study, the five attributes tested by panelists are given in Table 6. Except for barely detected unpleasnt odour (barely vinegar like odour) scores, sensory attribute of cooked Tilapia treated with acetic acid did not differ significantly compared with control (p‹0.05).In this respect, Marshall and Kim (1996) stated that catfish fillets treated with 2% acetic acid for 5-60seconds were liked less by sensory panels than control due to acidic odour. The detected vinegar-like odour in treated fish in our study did not significantly affects the overall acceptability compared with control, and judged as acceptable Table 6. Ahmed (1999) concluded that acetic acid should not be used in concentration higher than 2% because consumer may reject such acid treated fish as they alter sensor quality especially odour and color of such fish. our experiment revealed that with 5 % acetic acid fish still acceptable by panelists and that may lead to the fact that intact fish less affected by acid than filleted fish.
CONCLUSION
From the present study it could be concluded that the fresh water fishes (O. niloticus) are subjected to infection with Cryptosporidium, Acanthocephalus and encysted metacercariae of different trematode worms, which could be transmitted to the consumers causing dangerous disease. Therefore such parasites must be well controlled in order to avoid their transmission to man. This study also revealed that some fish processing methods or treatments are adequate to kill ECM in O. niloticus. Storage of fish at -10 ˚C for 12 hour, marination of fish in 5% acetic acid for one minute and waiting for 2 hours or dry salting for one hour using table salt (sodium chloride /fish=3gram/10gram).
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دراسات على الکريبتوسبوريديم وبعض الطفيليات الأخرى التي تصيب الإنسان في اسماک البلطي النيلي في محافظه أسيوط
محمود عمار محمدعمار, محسن إبراهيم عرفة
Email: mohsenpara22@yahoo.com
تم إجراء هذه الدراسة علي 120 عينة من أسماک البلطي الطازج (60 بلطي مزارع و60 بلطي من نهر النيل) والتي تم جمعها من أماکن متفرقة من محافظة أسيوط وذلک بهدف دراسة مدي تواجد طفيل الکربتوسبوريديم وبعض الطفيليات الأخرى التي تصيب الإنسان وکذلک دراسة التأثيرات المختلفة لملح الطعام ، حمض الخليک ، الخل والتبريد علي الطور اليرقي المتحوصل. بفحص عينات الخياشيم ، العضلات والقناة الهضمية لتلک الأسماک تبين تواجد الطفيليات في الأسماک النيلية المصدر بمعدل أعلي (80%) مقارنة بأسماک المزارع ( 55%) کما تواجدت الطفيليات المختلفة في اسماک البلطي النيلي واسماک المزارع علي النحو التالي: الکربتوسبوريديم 15% ، 23.3 % , الاکانثوسفلا 8.3 ، 9.2 % الطور اليرقي المتحوصل الميکروسکوبي 88.3 ، 26.7 % علي التوالي. بينما تواجد الطور المتحوصل العيني في البلطي النيلي المصدر فقط وبنسبة 40%. بدراسة التأثيرات المختلفة علي الطور اليرقي المتحوصل (الميتاسرکاريا) في العضلات للديدان المفلطحة تبين الآتي : بغمر قطعة من عضلات الأسماک المحتوية علي الطور اليرقي المتحوصل النشط بترکيزات مختلفة من محلول ملح الطعام ، حمض الخليک والخل التجاري نتج فقد لحيوية الطور اليرقي المتحوصل بعد 1 ، 2 ساعة من الغمر في ترکيز 30 ، 20 % من ملح الطعام علي التوالي ، 1 ، 6 ، 12 ساعة من الغمر في محلول حمض الخليک ترکيز 5.00 ، 2.50 ، 1.25 % علي التوالي ، بينما لم تتأثر حيوية الطور اليرقي المتحوصل بالغمر في محلول الخل التجاري ترکيز 5% لمدة 24 ساعة. والتمليح الجاف باستخدام ملح الطعام نتج عنة فقد لحيوية الطور اليرقي المتحوصل بعد ساعة واحدة من التمليح. بحفظ الأسماک عند 5 درجه مئوية لمدة 24 ساعة لم تتأثر حيوية الطور اليرقي المتحوصل بينما حدث فقد للحيوية عند حفظ الأسماک عند ( -10) درجه مئوية لمدة 12 ساعة. وبغمر الاسماک في محلول حمض الخليک بترکيز 5% لمدة دقيقة ، فقد الطور المتحوصل حيويته بعد ساعتين من المعاملة وتبع ذلک انخفاض معنوي (p<0.05) في الاس الهيدروجيني (pH) مع اکتساب رائحة الخل عند الفحص الحسي للأسماک المعاملة بحمض الخليک مقارنة بالأسماک الضابطة للتجربة ولکن ظلت مقبولة لدي (Sensory evaluation panelist) مجموعة التقدير الحسي.