| Literature DB >> 30519613 |
Zahra Derakhshan1, Amir Hossein Mahvi2,3, Mohammad Faramarzian1, Mansooreh Dehghani1, Marjan Salari4, Yadolah Fakhri5, Mojtaba Afsharnia6, Motahareh Sadat Hosseini7, Ameneh Marzban8, Mahmoud Taghavi6.
Abstract
Food contamination by heavy metals can lead to the accumulation of these elements in the body of consumers and the contraction of diseases. Accordingly, heavy metal concentration in common carp fishes consumed in Shiraz, Iran was determined in the present study. The mean concentrations of Pb, Cd, Zn, and Cu were 0.23, 0.07, 0.47, and 0.59 mg/kg (dry weight), respectively. The average concentration of heavy metals in the muscle of common carps consumed in Shiraz was less than the permissible standard of the WHO and FAO. The estimated weekly intake (EWI) of the studied metals was below the provisional tolerable weekly intake (PTWI). The maximum and minimum relative risk (RR) equaled 48.93 and 0.55% of the total risk for Cd and Zn, respectively.Entities:
Year: 2018 PMID: 30519613 PMCID: PMC6260411 DOI: 10.1016/j.dib.2018.11.029
Source DB: PubMed Journal: Data Brief ISSN: 2352-3409
Maximum heavy metal limit in fish muscles (mg/kg) according to international standards [13], [14], [15].
| Organization | Metals | |||
|---|---|---|---|---|
| Pb | Cd | Zn | Cu | |
| FAO (1983) | 0.5 | 0.05 | 30 | 30 |
| FAO/WHO limit | 0.5 | 0.5 | – | – |
| WHO 1989 | 2 | – | – | – |
| European Commission Regulation | 0.3 | 0.05 | ||
| Chinese Food Codex | 0.5 | 0.1 | – | – |
Fig. 1Concentration of heavy metals in the muscle tissue of carp fish.
The estimated EDI and EWI in Fars population through the consumption of common carp fish.
| PTWI (mg/ kg bw /week) | EDI (mg/ kg bw /day) | EWI (mg/ kg bw /week) | %PTWI | |
|---|---|---|---|---|
| Pb | 0.025 | 0.18 × 10−4 | 1.30 × 10−4 | 0.52 |
| Cd | 0.007 | 0.06 × 10−4 | 0.40 × 10−4 | 0.56 |
| Zn | 7 | 0.38 × 10−4 | 2.65 × 10−4 | 0.003 |
| Cu | 3.5 | 0.47 × 10−4 | 3.33 × 10−4 | 0.009 |
Makedonski et al. [16].
Carcinogenic and non-carcinogenic daily consumption rate limit (CRlim), maximum allowable consumption rate (CRmm), target hazard quotient (THQ), cancer slope factor (CSF), cancer risk (CR), and relative risk (RR) for the consumption of common carp fish in Shiraz, Iran.
| Metal | RfD (mg/kg bw/day) | Non-carcinogenic rate limit | Carcinogenic rate limit | THQ | CSF (mg/kg/day) | CR | RR (%) | ||
|---|---|---|---|---|---|---|---|---|---|
| CRlim (kg/day) | CRmm(meals/month) | CRlim(kg/day) | CRmm(meals/month) | ||||||
| Pb | 0.02 | 0.56 | 75 | 0.33 | 44 | 9.27 × 10−3 | 8.5 × 10−3, | 1.57 × 10−7 | 40.20 |
| Cd | 0.0005 | 0.46 | 62 | – | – | 5.54 × 10−3 | – | – | 48.93 |
| Zn | 0.3 | 41.48 | 5563 | – | – | 12.63 × 10−3 | – | 0.55 | |
| Cu | 0.04 | 4.40 | 590 | – | – | 2.38 × 10−3 | – | – | 10.32 |
Taweel et al. [17].
Miri et al. [13].
Fig. 2The location of the study area, i.e. Shiraz, Fars Province, Iran.
| Subject area | Environmental science |
| More specific subject area | Environmental monitoring, food quality |
| Type of data | Tables, figure |
| How data was acquired | Atomic Absorption Spectroscopy (Varian AA-7000) |
| Data format | Raw/analyzed |
| Experimental factors | Heavy metal concentration |
| Experimental features | Daily intake of heavy metals was determined. |
| Data source location | Shiraz, Fars Province, Iran |
| Data accessibility | The data are available in this article. |
| Related research article | Health risk assessment of heavy metal intake due to fish consumption in the Sistan region, Iran. 2017; Environmental Monitoring and Assessment 189(11),583 |