Bioaccumulation of zinc in crops and its contribution to Zn intake by Cuban population

Bioacumulación de zinc en cultivos y su contribución a la ingestión de Zn por la población cubana

Oscar Díaz Rizo¹, Susana Olivares Reumont¹, Otoniel Denis Alpízar², Lázaro Lima Cazorla¹, Katia D´Alessandro Rodríguez¹ , Juana O. Arado López¹  

odrizo@instec.cu

ABSTRACT

Zinc content and Zn bioaccumulation in crops (rice and some vegetables and condiments) cultivated in 18 Cuban urban and suburban areas are reported. Zinc content in food and the corresponding farming soil samples was determined by X-Ray Fluorescence analysis and by Atomic Absorption spectrometry. The quality of the analysis was verified using the Certified Reference Materials IAEA 393 «Algae», MA-B-3/TM «Fish Tissue Lyophilised», IAEA V-10 «Hay» and IAEA Soil-7. The obtained results show rice, of the studied crops, as the major Zn bioaccumulator and important Zn source in Cuban human diet.

Key words: Cuba, diet, biological accumulation, soils, crops, X-ray fluorescence analysis, absorption spectroscopy

RESUMEN

Palabras claves: Cuba, dieta, acumulación biológica, suelos, cosechas, análisis por fluorescencia de rayos X, espectroscopia de absorción.

INTRODUCTION

Trace elements play an important role in human nutrition and health, and hundreds of millions of people around the world suffer the consequences of trace element deficiencies [1]. Among those, zinc is an essential microelement, which people solely ingest from their diet. The World Hearth Organization (WHO) recommends a daily optimal intake for adults of 12-15 mg of zinc [1]. Zinc influences cell division, growth and development as well as sexual maturation. It is also a membrane stabilizer and essential for the integrity of the immune system [2]. Moreover, zinc is required by more than 100 enzymes as cofactor, and it seems to help in the proper storage and release of insulin, growth and repair of tissues, the ability to taste food, mineralization of bone, blood clotting, the function of vitamin A and the functions of the thyroid hormones [3]. Inadequate zinc nutrition is becoming a considerable public health problem nowadays, with the WHO lastly highlighting zinc deficiency as one of the 10 major factors contributing to the burden of disease in developing countries [4].

Rice is the main garniture in Cuban diet, with population consuming (in average) around 200 grams per day. However, urban and suburban agriculture in Cuba have accomplished a considerable increment in the ingestion of fresh vegetables (tomato, lettuce, cabbage, cucumber, gumbo, etc.) in the last decades [5]. Furthermore, garlic, onion, red pepper and parsley are quite popular condiments in Cuban cuisine. The present study summarizes zinc content determination in regular consumption foodstuff (rice, some vegetables, fruits and condiments) and its corresponding farming soils using nuclear and related techniques in order to determinate its contribution to the net Zn intake within the Cuban population's diet.

MATERIALS AND METHODS

The edible parts of different crops (rice, vegetables, fruits and roots samples) and its corresponding farming soils were collected in 18 urban and suburban agricultural areas from La Habana, Matanzas and Cienfuegos cities. Composite samples, consisting on four subsamples, were collected at each site (approximately 5 x 5 m). Zinc concentrations in soils were estimated by X-Ray Fluorescence Analysis (XRF) using Certified Reference Materials (CRM) as standards, a (1.1 GBq) excitation source with ring geometry and a Canberra Si(Li) detector-based XRF spectrometer at Nuclear Analytical Lab at InSTEC (150 eV energy resolution at 5.9 keV, Be window thickness = 12.0 mm) coupled to a MCA, following the methodology described in [6]. On the other hand, the zinc content in rice samples was determined by XRF using set of Zn-doped cellulose samples for calibration [7], while Zn contents in the rest of the crops was determined by AAS (Buck Scientific 210 VGP) according to the procedure established and validated in the Environmental Analytical Lab at InSTEC [8] (PNO09 2007).

where –experimental value, –certified value and s is the standard deviation of . On the basis of this criterion, the similarity between the certified value and the analytical data obtained by the proposed methods is divided into three categories: SR 25% = excellent; 25 < SR 50% = acceptable, SR > 50% = unacceptable. The analysis of five replica of the CRMs IAEA 393 «Algae», MA-B-3/TM «Fish Tissue Lyophilised», IAEA V-10 «Hay» and IAEA Soil-7 is presented in Table 1. Both, XRF and AAS methodologies, show “excellent” (SR 25%) results and a very good correlation (R = 0.999) between the certified and measured values.

In order to estimate the rate at which Zn appears in the selected specie and associated soil, the biota-soil bioaccumulations factors (BFs) were calculated in the studied samples according to the formula [10]:

where and are the mean concentrations of Zn in the food sample and its corresponding soil, respectively.

RESULTS AND DISCUSSION

Zinc content in all studied food samples are shown in Table 2. The highest mean content and bioaccumulation values were found in the studied rice samples (35.9 fresh weight and 41.0%, respectively), while the lowest content was found in tomato fruits. As it is well known, rice is one of the most frequently consumed cereals worldwide, especially in developing countries. For this reason, in the last decade different studies were performed (supported by FAO) in order to solve the Zn deficiency in rice. For example, positive results were obtained by doping rice seeds with or using Zn doped fertilizers [11] and applying biotechnological techniques to increase the essential metal absorption by plants [12]. Cuba was part of these FAO studies evidencing the high Zn content in our cultivated rice. Thus, around the 70% of the established Zn daily intake by Cuban regulations (1 body weight ) [13] is supplied by rice consumption.

For the rest of the studied crops (vegetables and condiments), the determined Zn concentration (and the corresponding bioaccumulation) is very low when compared to rice Zn content and bioaccumulation. The concentration values are similar to those reported by other authors and, for the major part of the studied fruits and vegetables, the Zn content does not exceed its maximum allowable limit (10.0 fresh weight) specified by Cuban regulations [13]. In the studied vegetables, on average, higher zinc content was found in those with leaves as edible parts (Figure), compared with vegetables of which edible parts are roots and fruits.

In Cuba, from the studied vegetables, only lettuce, cabbage, onions, tomato, red pepper and cucumber are frequently consumed. Assuming an average daily consumption (in one month) of rice – 200 g, vegetables whose edible parts are leaves – 100 g, vegetables whose edible parts are roots – 100 g and vegetables whose edible parts are fruits – 100 g, the Daily Dietary Intakes (DDI) of Zn in Cuba would be around 8.8 mg per day. This value is similar to the recommended medium level for Zn intake (8.7 mg per day) [1] and it is the 80% of the US Recommendable Dietary Allowances (11.0 mg per day) [22].

This seems to indicate that Cuban population would be able to meet the normative requirements if consuming diets of uniformly low zinc bioavailability. It is also apparent that dietary intake data taken alone (without consideration of the bioavailability) does not allow a reliable assessment of whether a particular population has an adequate or inadequate nutrition.

The bioavailability of zinc from different diets depends on many factors. High availability is found only in refined diets low in cereal fibre and phytic acid contents, and with adequate proteins, mainly from non-vegetable sources such as meat and fish. Therefore, Zn content in meat and fish tissues remains to be assessed by a specific study to estimate a more accurate Zn DDI of the Cuban population.

CONCLUSIONES

REFERENCES

1. WORLD HEALTH ORGANIZATION. Trace Elements in Human Nutrition and Health. Geneva: WHO, 1996.
2. SCHLESINGER L, AREVALO M, ARREDONDO S, et. al. Effect of a zinc-fortified formula on immunocompetence and growth of malnourished infants. Am J Clin Nutr. 1993; 56(3): 491-498.
3. HANDS ES. Nutrients in food. London: Lippincott Williams and Wilkins, 1999.
4. PARR RM, ARAS NK, IYENGAR GV. Dietary intakes of essential trace elements: Results from total diet studies supported by the IAEA. J Radioanal Nucl Chem. 2006; 270: 155-161.
5. ALTIERI MA, COMPANIONI N, CAÑIZARES K, et. al. The greening of the “barrios”: urban agriculture for food security in Cuba. Agric Hum Values. 1999; 16(2): 131-140.
6. DÍAZ RIZO O, ECHEVARRÍA F, ARADO JO, MERLO M. Assessment of heavy metal pollution in urban soils of Havana city, Cuba. Bull Environ Contam Toxicol. 2011; 87(4): 414-419.
7. DENIS ALPÍZAR O, DÍAZ RIZO O. Zinc content in rice and other agriproduct by X-ray fluorescence. Nucleus. 2009; (46): 34-39.
8. InSTEC. Cd, Pb, Zn and Cu content determination in fresh vegetables.  Quality Assurance System of the Environmental Analytical Laboratory. Procedure No. 9 (PNO09). La Habana: InSTEC, 2007 (in Spanish).
9. QUEVAUVILLER Ph, MARRIER E. Quality Assurance for Environmental Analysis In:
Quality    Assurance for Environmental Analysis. Tech. Instrum. Anal. Chem. 1995, 17: 1-25.
10. VIVES A, MOREIRA S, BRIENZA S, et. al. Synchrotron radiation total reflection X-ray fluorescence (SR-TXRF) for evaluation of food contamination. J Radioanal Nucl Chem. 2006; 270(1): 147-153.
11. SLATON NA, NORMAN R, WILSON CE. Effect of zinc source and application time on zinc uptake and grain yield of flood-irrigated rice. Agron J. 2005; 97: 272-278.
12. CAKMAK I. Plant nutrition research: Priorities to meet human needs for food in sustainable ways. Plant Soil. 2002; 247: 3-24.
13. NORMA CUBANA-493. Metallic contaminant in food-sanitary regulation. Cuban National Bureau of Standards. ICS:67.020, Havana, Cuba, 2006 (in Spanish).
14. KABATA-PENDIAS A, PENDIAS H. Trace element in soils and plants. Boca Raton: CRC Press, 1992.
15. BAHEMUKA T, MUBOFU E. Heavy metals in edible green vegetables grown along the sites of the Sinza and Msimbazi rivers in Dar es Salaam, Tanzania. Food Chem. 1999; 66(1): 63-66.
16. GORBUNOV A, FROTASYEVA M, KISTANOV A, et. al. Heavy and toxic metals in  staple foodstuffs and agriproduct from contaminated soils. JINR Communication E18-2002-111. Dubna:  JINR, 2002.
17. BOSIACKI M, TYKSINSKI W. Copper, zinc, iron and manganese content in edible parts of some fresh vegetables sold on markets in Poznan. J Elementol. 2009; 14(1): 13-22.
18. PANDEY J, PANDEY U. Accumulation of heavy metals in dietary vegetables and cultivated soil horizon in organic farming system in relation to atmospheric deposition in a seasonally dry tropical region of India. Environ Monit Assess. 2009; 148(1-4): 61-74.
19. YUNG MC. Heavy metal concentrations in soils and factors affecting metal uptake by plants in the vicinity of a Korean Cu-W mine. Sensors. 2008; 8(4): 2413-2423.
20IYAKA YA. Concentration of Cu and Zn in some fruits and vegetables commonly available in north-central zone of Nigeria. EJEAFChe. 2007; 6(6): 2150-2154.
21. MARCUSSEN H, JOERGENSEN K, HOLM PE, et. al. Element contents and food safety of water spinach (Ipomoea aquatica Forssk.) cultivated with wastewater in Hanoi, Vietnam. Environ. Monit. Assess. 2008, 139(1-3): 77–91.
22. FOOD AND NUTRITION BOARD. Dietary Reference Intakes for Vitamin A, Vitamin K, Arsenic, Boron, Chromium, Copper, Iodine, Iron, Manganese, Molybdenum, Nickel, Silicon, Vanadium, and Zinc. Washington DC. National Academy Press, 2000.

Recibido: 22 de julio de 2013 ]]> Aceptado: 24 de octubre de 2013