Contamination of Cu, Zn, Fe and Mn in Katsuwonus pelamis (Linnaeus, 1758) from Karachi Fish Harbor and Potential Risks to Human Health

In the present study, skipjack tuna (Katsuwonus pelamis) from the Karachi coast between 2006 and 2011 were chosen and analyzed for the Fe, Mn, Cu and Zn levels in the edible dorsal tissues, livers, kidney, gills and gonads. The liver tissues had the highest concentrations of metals (623±103 mg kg-1 for Fe, 49±13 mg kg-1 for Mn, 67±17 mg kg-1 for Cu and 68±21 mg kg-1 for Zn). The muscle maximum concentrations of Fe, Mn, Cu, and Zn were 46±17, 6±2, 7±2 and 7±2 mg kg-1, respectively. The results revealed that Fe concentrations were higher than those of other metals. The values obtained were compared with the international regulation maximal allowable standards in seafood. The current work attested that calculated diurnal and hebdomadal intakes of Fe, Mn, Cu and Zn levels by way of consumption of skipjack tuna were not in excess of the Permissible Tolerable Daily Intake (PTDI) and Provisional Tolerable Weekly Intake (PTWI) values established by FAO/WHO. In conclusion, K. pelamis appears to be useful bioindicator due to their accumulation of the metals and continued sampling and pollution effects on food chain organisms comparatively are required for further investigations.


Introduction
The family Scombridae incorporates many of the world's most popular and commercial fishes. Tunas, mackerels and bonitos as a member of Scombrids are important sources of energy and protein and dietary associated with good health. In the Mediterranean countries, tunas have been caught locally for many years, yet intense commercial misuse of open-ocean tunas has led in some cases to decrease of tuna populations. Many of the tuna captured is used for canning (Anonymous, 2017). Pakistan has a coastline of well -nigh 990 km throughout with contiguous coastal zone of 240,000 km 2 in Northern Arabian Sea. Its' coastal zone has rich living and non-living resources. The Karachi coastline of Pakistan accelerating pollution grade which is related to the extending of the shipping industry via port, is heavily contaminating the mangrove and aquatic life. Industries produce great amount of their waste (Anonymous, 1991a). Untreated contaminant and sewage are discharge into the marine coasts alongside oil spills from ships and fishing activities through the port. (Anonymous, 1991b). The Karachi coast is subject to pollution owing to anthropogenic activities such as domestic and industrial effluents, shipping and fishing activities, and consolidated chemicals from agricultural run-off from various hot spots (Rizvi et al., 1988;Saleem and Kazi, 1995;1998;Saifullah et al., 2002). Most of the coastal pollution is condensed in the Karachi harbour where an approximated 90,000 tons of oil products from ships and seaport are drained off every year. Fish are the upper of the marine food chain and may bioconcentration of great quantities of some metals from surrounding water (Mansour and Sidky, 2002). In contaminated marine coastal environments, fish may be accumulated the metals in their edible tissue 2015d;2015e;2015f). Metal levels in the fishes determined as biomarkers can render as an index of the biologically existing metal burden. Hereby the metal levels in the edible tissues of fish can ensure a criterion for the extent of pollution in coastal waters. Muscle is a fish tissue mostly selected for assay because of edible tissue . In addition to this, liver is a vital organ for metals storage 2015e; and purge in fishes where the synthesis of metallothionein induced by metals occur (Boudou and Ribeyre, 1989). Other organ that may be regarded for assay is the gill, which is in steady contact with the surrounding water and the metals contained therein (Ahmed and Bat, 2015e;. Fish is a major source of protein and gain for people living in the south-eastern Asia. However, detrimental substances such as metals released by anthropogenic activities have contaminated the marine coastal environment. For example, the Straits of Malacca, a momentous fishing place (Eng et al., 1989) is badly polluted by international shipping activity, intense industrialization and urbanization, and oil spills (Eng et al., 1989;Abdullah et al., 1999). The main aim of the current study to determine Fe, Mn, Cu and Zn concentrations in Katsuwonus pelamis collected from Karachi fish harbour (Figure 1).

Materials and Methods
K. pelamis specimens of similar sizes were collected seasonally between August 2006 and December 2011. After biometric measurements, specimens were dissected using steel scissors and scalpels to take about 5 g edible muscles, entire organs (liver, kidney and gonads) and two rakers of gills. They were cleaned with deionized water and weighed (modified from UNEP, 1984;Tuzen, 2003;Karadede et al., 2004;Papagiannis et al., 2004). The specimens were crushed and calcinated at 500 o C for three hours til they turned to white or grey. Then they were prepared with respect to the procedure of Gutierrez et al. (1978). The cinders were melted in 10 ml (HCl) in beakers and which the residues were filtered with Whatman filter paper and after were diluted to 25 ml distilled water with 1 N HNO 3 . The equipment AAS Perkin Elmer, model AAnalyst 700, USA, with background adjustment and acetylene as fuel were initiated and presented programme win lab 32 software. The absorption wavelengths (nm) for Cu, Zn, Fe and Mn were 324.7, 213.9, 248.3 and 279.5, respectively. The detection limits of Cu, Zn, Fe and Mn were 0.23, 0.50, 0.45 and 0.58 ppb, respectively. At least three standards from 1000 ppm stock solution to 2, 4 and 6 ppm were made. The equipment together with the referred standards were calibrated. The specimens severally were aspirated to determine Cu, Zn, Fe and Mn levels. A one-way analysis of variance (ANOVA) in which the within sample variances and between the sample variances were employed to regard the initial step interactions between the organs, year and seasons (Snedecor and Cochran, 1967). The Bonferroni test was applied for correction to set agains the problem of multiple comparisons. All values were expressed as µg metal g dry wt.
Analyses for the obtained results of metals are shown in Table 6 and Table 7.

Remarks
The heavy metal pollution of marine environment may be evaluated by analysing seawater, sediments and biota. Because of metal levels in marine organisms are generally notably higher than those in other items of marine ecosystem (Bryan, 1976;Phillips and Rainbow, 1994). Phillips (1980) represented that for an organism to be a good indicator of metal contamination, there should be a simple correlation between metal values in the surroundings and in the organism. Fish are broadly chosen as sentinels of pollution in marine coastal area (Bat, 2014;Ahmed and Bat, 2016a;2016b;Ahmed et al., 2016) and may accumulate metals over background levels and so, verify their likely as biomonitors of heavy metal pollution . Most living being need minor quantities of many essential metals such as iron, manganese, copper and zinc for their vital processes (Bryan, 1976). Besides, these ones have toxic when they passed over definite limits (Rainbow, 1985). In the present study, the concentrations of Cu, Zn, Fe and Mn have been measured in skipjack tuna (K. pelamis) collected from Karachi fish harbour of Arabian Sea. Skipjack tuna is a pelagic fish and is the top of food c hain. They feed on mainly fish, crustaceans, cephalopods and mollusc (Kojadinovic et al., 2007;Jakimska et al., 2011). It is also notified that metabolic rates (Korsmeyer and Dewar, 2001) and digestion and growth rates  of the pelagic fish are three and two to five folds higher than those of many fish species of same length, respectively. Because of their high rates of metabolism and xenobiotic uptake (Kojadinovic et al., 2007;Jakimska et al., 2011), it may results in a rise in the concentrations of heavy metal taken up and hence accumulated. Bustamente et al. (2003) pointed out that difference in metal levels coupled with food and nutrition temperaments of benthic and pelagic fish species and found that benthic fish generally accumulated higher metal levels than those in pelagic fish. This finding is disagreeing with the results of Topping (1973) who put forwarded that primarily plankton nourishment fish comprise much higher metal levels than those benthic nourishment fish from Scottish waters. Jakimska et al. (2011) found that carnivorous species accumulated higher heavy metals than herbivores and omnivores. These results are similar to Bat et al. (2012a) which show high heavy metal levels in sprat which is pelagic and zooplanktonivorous fish and has high metabolic rate. This makes skipjack tuna ideal bioindicator for assessing heavy metal pollution in marine ecosystems (Kojadinovic et al., 2007). Heavy metal levels varied among the tissues and organs with seasonally. This may be attributed to factors such as water temperature and food. The data in Table 2, Table 3, Table 4 and Table 5 on the dispersion of the metal levels in the organs and tissues of the skipjack tuna represent that there is a significant concentration of these metals in liver than those in edible parts. These findings were similar to those reported by other studies in Karachi coasts (Yousuf et al., 2013;Ahmed et al., 2014). This is also agreed with the study of Bat et al. (2012b) that heavy metal levels of bottom fish Psetta maxima in liver were greater than those in edible tissues and gonad for both male and female, recommending that liver is an organ in which metals are accumulated. The results for these metals also demonstrated that there was disparity in metal levels seasonally. Fe is the maximum available in large quantities of the metals investigated. In skipjack tuna, gill was the second target tissue for Mn and Cu. Dallinger et al. (1987) emphasizes that one of the major route of heavy metal assimilation in fish are water, through the gills. It is interesting to note that Zn in muscle tissue is higher than those in in gills and gonads. Cu in muscle tissues is also greater than those in gonad. From the current study, gonads generally accumulated low heavy metals except Fe. Maximum Cu and Zn levels in dorsal muscles were 7±2 μg/g dry wt. Statutory thresholds are not existing for requisite elements in European countries. Nevertheless, in the edible tissues of skipjack tuna the mean metal levels were beneath the maximal allowance values for people consumption set by compared the international regulations (Table 8). The Cu and Zn levels in kidney, gills and gonads were always lower than the permissible maxima, but liver Cu and Zn levels exceeded the allowable levels. It should be noted that the concentrations of metals were given as dry wt. in the present study. Even so it is recommended that the liver of skipjack tuna should be ejected and decently cleaned before consumption.  According to the current study results Estimated Weekly Intake (EWI) and Estimated Daily Intake (EDI) for a 70 kg person weight were submitted in Table 10 and were incorporated with standards in Table 9 for evaluation of these metals in K. pelamis. The Joint FAO/WHO Expert Committee on Food Additives set PTWIs for both Cu and Zn were had in Table 9, which was tantamount to 245 and 490 mg/week for a 70 kg person, respectively. The main per diem fish consumption in Pakistan is 5 g per individual (Anonymous, 2010b). It is withal equal to 35 g/week. By calculating the averages of weekly fish eaten in Pakistan and the most Cu and Zn values in skipjack tuna, weekly entrance counted per body for these metals in edible muscles of K. pelamis. As it can be deduced out of the Table 10, the evaluated EWIs of both Cu and Zn in the current work is rather under the approved safe levels.

Conclusion
The present study had for objective to measure levels of the metals namely Fe, Mn, Cu and Zn in skipjack tuna ( K. pelamis) from the Karachi coast between 2006 and 2011. The means levels of these metals varied depending on seasons. The weekly intakes of Cu and Zn per kg of person amounts not passed over the Provisional Tolerable Weekly Intake (PTWI) established. The heavy metal concentrations of skipjack tuna in Karachi fish harbour of Arabian Sea do not present any danger to people consumption. These information ensure a beneficial reference line to gage essential these metals any oncoming alters in local pollution. It is also suggested that the commercial fish used as pollution bio-indicators for assessment of environmental health of coastal areas.