Abstract
The study aimed to verify whether canned fish available in Poland were safe in terms of Cd and Pb content. The content of Cd and Pb was examined in 25 products using Graphite Furnace Atomic Absorption Spectrometry (GFAAS). The examined canned fish contained from nearly 0.2 to 1.7 μg Cd and from ca. 0.02 μg to ca. 7.9 μg per 100 g of the product. The content of both Cd and Pb was found to be higher in canned salmon and tuna. It was found that consumption of canned fish acute posed no hazard to adult men. Consuming 1 canned fish a week will result in an intake of Cd amounting to a maximum of 0.8 % TWI, and of Pb amounting to a maximum of 3.5 % BMDL10 and 1.23 % BMDL01. The levels of Cd and Pb in canned fish do not exceed safe levels for men.
Avoid common mistakes on your manuscript.
1 Introduction
Aqueous environment is particularly exposed to pollution, since water reservoirs are often a direct destination for the discharge of process effluents, municipal wastewater sewage and pollutants from farming activity. Fish are one of the last cells within the trophic network of aqueous ecosystems so significant amounts of toxic metals can accumulate in their tissues. The content of metals in organisms is determined by: amount of exposure (dose), route of absorption, rate of excretion, and eating habits. Cadmium (Cd) and lead (Pb) are characterised by an ability to accumulate in tissues and a long half-life. Cadmium can cause kidneys damage whereas lead has been associated with kidneys diseases and with the central nervous system damage (EFSA 2012a, b). These metals show a mutagenic, genotoxic, carcinogenic and teratogenic effect on humans and animals.
Despite potential hazards related to consumption of fish by humans, fish meat is recommended as an excellent source of complete protein, polyunsaturated fatty acids, minerals and vitamins (Usydus et al. 2009). According to rational nutrition guidelines, meals comprising 200–300 g of various fish species should be consumed 2–3 times a week. The presented study was to verify whether canned fish available in Poland were safe in terms of Cd and Pb content. This group of fish products was selected with regard to the fact that canned fish is very convenient to eat, microbiologically safe and is a frequent choice among consumers in Poland—canned fish accounts for as much as 60 % of all fish products (Usydus et al. 2009).
2 Materials and methods
2.1 Materials
Canned fish (n = 25) were purchased in grocery shops in Lublin from May to July 2012. The cans contained tuna (n = 6), mackerel (n = 5), herring (n = 6), sprat (n = 4) and salmon (n = 4) (Table 1). Prior to sampling the contents were thoroughly mixed using a homogenizer to make the mixture uniform throughout. Afterwards, three samples of ca. 3 g were taken from each product.
2.2 Determination of the content of Cd and Pb
The samples were dried at a temperature of 105 °C and then ashed at a temperature of 450 °C (Winiarska-Mieczan 2014). The content of Cd and Pb was determined by Graphite Furnace Atomic Absorption Spectrometry (GFAAS) in a Zeeman Varian Spectr AA 880, using the following parameters:
Cd: λ = 228.8 nm; LOQ 0.004 mg/kg; LOD 0.001 mg/kg
Pb: λ = 217.0 nm; LOQ 0.03 mg/kg; LOD 0.011 mg/kg.
More than 94 % Cd and Pb was recovered from the reference material with about 5 % replicability of results. The results were verified against a blank sample (1 M HNO3) and CRM DORM-3. Standard Cd and Pb solutions were purchased from Merck (Germany). A detailed description of methods for determining Cd and Pb is provided in another work (Winiarska-Mieczan 2014).
2.3 Survey
The survey was carried out in October and November 2013 involving 350 men aged 19–24 from the student community of Lublin. The objective of the survey was to collect information about the popularity and amount of weekly intake of canned fish as well as about the respondents’ preferred choices.
2.4 Calculations
The content of Cd and Pb was calculated as per fresh weight of the product. The weekly supply of Cd and Pb from canned fish was calculated assuming that an adult man weighing 70 kg consumes 1 can of fish/week. Information concerning the intake of canned fish was obtained by survey. This enabled calculating the actual intake of Cd and Pb from canned products. The standard values proposed by EFSA (European Food Safety Authority) were adopted: TWI (Tolerable Weekly Intake) for Cd—2.5 μg/kg of body weight/week and two BMDL (Benchmark Dose Lower Confidence Limit) values for Pb: BMDL10—4.4 μg/kg of body weight/week and BMDL01—10.5 μg/kg of body weight/week for nephrotoxicity and cardiovascular effects (EFSA 2012a, b).
3 Results
3.1 Popularity of canned fish
The survey showed that nearly all respondents (96.4 %) consumed canned fish, out of which 27.9 % of surveyed men ate such products once a week, 4.5 % a few times a week and 67.6 % sporadically. As many as 58.3 % of respondents reported that they preferred the taste of canned fish to that of fresh fish and could successfully replace them. The respondents’ most frequent choice was tuna and mackerel (ca. 50 % indications each). Their favourite addition was oil (more than 80 % indications), followed by tomato sauce (ca. 70 % indications) (Fig. 1a, b). Regardless of the frequency of fish consumption all respondents claimed they ate 1 can of fish at a time.
3.2 Content of Cd and Pb in canned fish
The examined canned fish contained from nearly 0.2 μg (sprat in tomato sauce) to 1.7 μg (tuna in olive oil) Cd per 100 g of the product (Table 1). The content of Pb per 100 g ranged from ca. 0.02 μg (herring in tomato sauce with pepper and fried herring in tomato sauce with pepper) to ca. 7.9 μg (tuna with vegetables in tomato sauce and royal salmon). The content of both Cd and Pb was found to be higher in canned salmon and tuna.
3.3 Safety of canned fish for consumption
A single can of salmon on average contained 2.14 μg Cd and 10.7 μg Pb, tuna—2.41 μg Cd and 7.71 μg Pb, while a can of mackerel—0.75 μg Cd and 5.3 μg Pb (Fig. 2a). The level of Cd in a can of herring and in that of sprat did not exceed 0.25 μg, and that of Pb—0.21 μg per can. Consuming 1 can of fish a week will result in an intake of Cd not exceeding 1 % TWI, and that of Pb lower than 3.5 % BMDL10 and 1.3 % BMDL01 (Fig. 2a). Tuna and salmon had the highest share in the supply of Cd and Pb (ca. 0.8 % TWI, 2.5–3.5 % BMDL10, 1–1.2 % BMDL01).
4 Discussion
Canned fish are among the favourite fish products for Poles (Usydus et al. 2009). These authors’ survey has shown that nearly 100 % of the audited population of young men ate canned fish.
The presented studies indicated that fish products available in the Lublin market were safe for adult male consumers in terms of Cd and Pb content. The highest content of the metals was found in canned tuna and salmon, which is not surprising considering these are predatory fish. The level of toxic metals increases at subsequent levels of the food chain as these metals tend to accumulate in tissues (Squadrone et al. 2013). Studies by other authors also revealed the presence of Cd and Pb in canned foods. Most available data refers to tuna as this species of fish is particularly popular among consumers around the world (Boadi et al. 2011), which was also supported by the present authors’ own studies.
The presented studies revealed that canned tuna contained 1.02–1.705 μg Cd and 1.19–7.89 μg Pb per 100 g. The content measured by other authors, based on research carried out in various countries (Ikem and Egeibor 2005; Boadi et al. 2011) was similar to that determined by the present authors; however, some authors obtained lower results (Mahalakshmi et al. 2012). In turn, results referring to the content of Cd and Pb in canned salmon and mackerel, available in literature (Ikem and Egeibor 2005), are lower compared to those obtained in these authors’ own studies. In own studies the lowest content of Cd and Pb was recorded in canned herring and sprats. These are fish from a lower level of the food chain, thus they accumulate less Cd and Pb.
The concentration of toxic metals in fish meat is primarily due to the pollution of the environment in which the fish live (geographical region), duration of exposure to the toxic agent and their diet (Squadrone et al. 2013). In addition, the material from which the can was made could be a source of contamination, although now a special varnish coat is often used inside the can to prevent metals from penetrating into the contents of the can (Taha´n et al. 1995). Suppin et al. (2005) demonstrated that the level of Pb in the meat of canned versus fresh fish differs to a slight degree only. In turn, in their studies involving 30 types of food, Al-Thagafi et al. (2014) found that the content of toxic metals in canned food was significantly higher than in the respective fresh food.
Results of these authors’ own studies indicate that weekly consumption of one can of salmon and tuna (that are most contaminated by Cd and Pb) does not add considerably to the amount of Cd and Pb taken up daily to the surveyed group of consumers as it will result in the supply of about 2.14–2.4 μg Cd and 7.7–10.7 μg Pb/day. On average, the supply of these metals from all the examined products does not exceed 0.16 μg Cd (0.39 % TWI) and 0.69 μg Pb (ca. 1.6 % BMDL) per day. This figure results from both the small content of metals in the products and low consumption of fish in Poland. Even if the above-mentioned canned fish are consumed at the recommended level (300 g/week), the risk of excessive intake of Cd and Pb seems negligible. Studies carried out in Spain showed that on average fish supply about 1.1 μg Cd and 2 μg Pd per day to adult men (Falcó et al. 2006). Studies in Lebanon demonstrated that fish eaten by adult residents in the amount of 17.9 g/day (of which 6.7 g was canned tuna) provided on average 0.1 μg of both Cd and Pb per day (Nasreddine et al. 2006). According to studies carried out among adult men from China, fish and seafood supply as much as 10.2 % Cd (He et al. 2013).
5 Conclusions
To sum up, results obtained by the present authors allow stating that the levels of toxic metals in canned fish do not exceed levels considered safe for the adults male population. Consumption of fish, also canned fish, should be promoted since fish are not very eagerly consumed in Poland. At the same time, due to the scarcity of data related to the content of toxic metals in canned foods in Poland, the impact of this method of food preservation on the content of Cd and Pb must be investigated.
References
Al-Thagafi Z, Arida H, Hassan R (2014) Trace toxic metal levels in canned and fresh food: a comparative study. Int J Innov Res Sci Eng Technol 3(2):8977–8989
Boadi NO, Twumasi SK, Badu M, Osei I (2011) Heavy metal contamination in canned fish marketed in Ghana. Am J Sci Ind Res 2(6):877–882
EFSA (2012a) Cadmium dietary exposure in the European population. EFSA J 10:2551–2588
EFSA (2012b) Lead dietary exposure in the European population. EFSA J 10:2831–2890
Falcó G, Llobet JM, Bocio A, Domingo JL (2006) Daily intake of arsenic, cadmium, mercury, and lead by consumption of edible marine species. J Agric Food Chem 54(16):6106–6112
He P, Lu Y, Liang Y, Chen B, Wu M, Li S, He G, Jin T (2013) Exposure assessment of dietary cadmium: findings from Shanghainese over 40 years, China. BMC Public Health 13:590 (11 pages). doi:10.1186/1471-2458-13-590
Ikem A, Egeibor NO (2005) Assessment of trace elements in canned fishes (mackerel, tuna, salmon, sardines and herrings) marketed in Georgia and Alabama (United States of America). J Food Compos Anal 18:771–787
Mahalakshmi M, Balakrishnan S, Indira K, Srinivasan M (2012) Characteristic level of heavy metals in canned tuna fish. J Toxicol Environ Health Sci 4(2):43–45
Nasreddine L, Hwalla N, El Samad O, Leblanc J-C, Hamze´ M, Sibiril Y, Parent-Massin D (2006) Dietary exposure to lead, cadmium, mercury and radionuclides of an adult urban population in Lebanon: a total diet study approach. Food Addit Contam 23(6):579–590
Squadrone S, Prearo M, Brizio P, Gavinelli S, Pellegrino M, Scanzio T, Guarise S, Benedetto A, Abete MC (2013) Heavy metals distribution in muscle, liver, kidney and gill of European catfish (Silurus glanis) from Italian Rivers. Chemosphere 90:358–365
Suppin D, Zahlbruckner R, Krapfenbauer-Cermak Ch, Hassan-Hauser Ch, Smulders FJM (2005) Mercury, lead and cadmium content of fresh and canned fish collected from Austrian retail operations. Nutrition 29(11):456–460
Taha´n JE, Sanchez JM, Granadillo VA, Cubillan HS, Romero RA (1995) Concentration of total Al, Cr, Cu, Fe, Hg, Na, Pb, and Zn in commercial canned seafood determined by atomic spectrometric means after mineralization by microwave heating. J Agric Food Chem 43:910–915
Usydus Z, Szlinder-Richert J, Polak-Juszczak L, Komar K, Adamczyk M, Malesa-Ciecwierz M, Ruczynska W (2009) Fish products available in Polish market—assessment of the nutritive value and human exposure to dioxins and other contaminants. Chemosphere 74:1420–1428
Winiarska-Mieczan A (2014) Assessment of the risk of exposure to cadmium and lead as a result of the consumption of low-fat dairy products by expectant and lactating women. Acta Sci Pol Technol Aliment 13(2):213–223
Author information
Authors and Affiliations
Corresponding author
Rights and permissions
Open Access This article is distributed under the terms of the Creative Commons Attribution License which permits any use, distribution, and reproduction in any medium, provided the original author(s) and the source are credited.
About this article
Cite this article
Winiarska-Mieczan, A., Kwiecień, M. & Krusiński, R. The content of cadmium and lead in canned fish available in the Polish market. J. Verbr. Lebensm. 10, 165–169 (2015). https://doi.org/10.1007/s00003-015-0933-0
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s00003-015-0933-0