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Revista Brasileira de Ciência do Solo

On-line version ISSN 1806-9657

Rev. Bras. Ciênc. Solo vol.35 no.1 Viçosa Jan./Feb. 2011

http://dx.doi.org/10.1590/S0100-06832011000100022 

NOTE

 

Evaluation of sample preparation methods and optimization of nickel determination in vegetable tissues*

 

Avaliação de métodos de preparo de amostra e otimização da determinação de níquel em tecidos vegetais

 

 

Rodrigo Fernando dos Santos SalazarI; Marco Aurélio Kondracki de AlcântaraII; Hélcio José Izário FilhoIII

IDoctorate student at Department of Chemistry, Universidade Federal de São Carlos – UFSCAR, Rodovia Washington Luiz Km 235, Monjolinho, CEP 13565-905 São Carlos (SP). E-mail: r.f.s.salazar@gmail.com
IIProfessor at the Department of Biotechnology, Escola de Engenharia de Lorena. Universidade de São Paulo – USP. EstradaMunicipal do Campinho s/nº, Campus I, CEP 12602-810 Lorena (SP). E-mail: marko@usp.br
IIIProfessor at the Departament of Chemistry Engeenering. Escola de Engenharia de Lorena. Universidade de São Paulo – USP. Lorena (SP), Brazil. E-mail: helcio@dequi.eel.usp.br

 

 


SUMMARY

Nickel, although essential to plants, may be toxic to plants and animals. It is mainly assimilated by food ingestion. However, information about the average levels of elements (including Ni) in edible vegetables from different regions is still scarce in Brazil. The objectives of this study were to: (a) evaluate and optimize a method for preparation of vegetable tissue samples for Ni determination; (b) optimize the analytical procedures for determination by Flame Atomic Absorption Spectrometry (FAAS) and by Electrothermal Atomic Absorption (ETAAS) in vegetable samples and (c) determine the Ni concentration in vegetables consumed in the cities of Lorena and Taubaté in the Vale do Paraíba, State of São Paulo, Brazil. By means of the analytical technique for determination by ETAAS or FAAS, the results were validated by the test of analyte addition and recovery. The most viable method tested for quantification of this element was HClO4-HNO3 wet digestion. All samples but carrot tissue collected in Lorena contained Ni levels above the permitted by the Brazilian Ministry of Health. The most disturbing results, requiring more detailed studies, were the Ni concentrations measured in carrot samples from Taubaté, where levels were five times higher than permitted by Brazilian regulations.

Index-terms: trace elements, atomic absorption spectrometry, calcination, wet digestion, environmental pollution.


RESUMO

O Ni, embora essencial às plantas, pode ser tóxico a estas e aos animais. O hábito alimentar é geralmente a sua principal via de obtenção. Contudo, informações sobre a composição média de elementos (incluindo Ni) em vegetais comestíveis em diferentes regiões ainda são escassas no Brasil. Os objetivos deste trabalho foram: (a) avaliar e otimizar um método para preparação de amostras de tecidos vegetais para a determinação de Ni; (b) otimizar os procediemntos analíticos para a determinação por espectrometria de absorção atômica por chama (FAAS) e por aquecimento eletrotérmico (ETAAS) em amostras vegetais; e (c) determinar a concentração de Ni em vegetais consumidos nas cidades de Lorena e Taubaté, no Vale do Paraíba, Estado de São Paulo, Brasil. Por meio da técnica analítica para determinação por ETAAS ou FAAS, os resultados puderam ser validados pelo teste de adição e recuperação de analito, sendo a digestão úmida com HClO4-HNO3 o método testado mais viável para quantificação desse elemento. Com exceção das amostras de cenoura coletadas em Lorena, todas as demais apresentaram teores de Ni acima do permitido pelo Ministério da Saúde do Brasil. Os resultados mais preocupantes e que demandam estudos mais detalhados referem-se aos teores de Ni nas amostras de cenoura da cidade de Taubaté, os quais foram superiores em cinco vezes aos limites estabelecidos pelas normas brasileiras.

Termos de indexação: elementos-traço, espectrometria de absorção atômica, calcinação, digestão úmida, poluição ambiental.


 

 

INTRODUCTION

Nickel is an element classified as essential to plants and, possibly, to animals (White & Brown, 2010). This element participates in the structure of the metalloenzyme urease, responsible for the decomposition of urea to ammonium and CO2 (Dechen & Nachtigall, 2006). On the other hand, this element may be toxic to plants and animals. According to White & Brown (2010), the minimum foliar concentration and the toxicity range for this element are 0.1 x 10-3 and 20 to 30 x 10-3 mg g-1 dry matter, respectively. The phytotoxicity of Ni is a result of its action on the photosystem, causing disturbances in the Calvin cycle and inhibition of electrical transport because of the excessive quantities of ATP and NADPH accumulated by the inefficiency of dark reactions (Krupa et al., 1993). The element may be considered moderately toxic to the human metabolism in comparison to other transition metals and, according to Wittsiepe et al. (2009), the biological role of this element in human metabolism is not evident. When inhaled or ingested, it may lead to serious complications, including cancer of the respiratory system (Ferreira et al., 2001; O'Neil et al., 2001).

Food ingestion is generally the main means of metal uptake. Nevertheless, information on the average composition of elements (including Ni) in edible vegetables from different regions is still scarce in Brazil (Kawashima & Soares, 2003; Santos et al., 2004). In several studies, as of Rocha et al. (2003) and Trannin et al. (2005), Ni concentrations (among other metals) in plants resulting from the addition of residues to the soil were determined. In the literature, studies as conducted by Schmidt et al. (2009) are rare, monitoring different metal contents in plants grown on soils in relation to the material of origin of a region (basalt and Caiuá sandstone). According to the Agency for Toxic Substance & Disease Registry (ATSDR), the estimated daily tolerable dosage of Ni for adults of 70 kg is 0.001–0.0024 mg kg-1 day -1 (ATSDR, 2010). Between 5 and 40 % of Ni present in foods is absorbed by the digestive tract, while, when inhaled, absorption oscillates from around 20 to 35 % (ATSDR, 2010). Data on metal concentrations in foods are therefore important and can provide basic information regarding the impacts caused by chemical products, effluents and residues used for crop maintenance and determine the levels of environmental pollution on family farms and agroindustrial farms. In the region of the Vale do Paraíba do Sul (in Taubaté, SP), contamination of maternal colostrum by Cd (Nascimento et al., 2005) and by Pb (Nascimento et al., 2006) has been detected recently in studies. In both studies, the authors warn that the possible sources of these metals must be identified.

Among the diverse methods for determination of minerals in vegetables, spectrometric techniques are among the most commonly used, due to their sensitivity and selectivity. The most widespread tool used with this technique is Flame Atomic Absorption Spectrometry (FAAS), produced by combustion of a mixture of air/acetylene or nitrous oxide/acetylene. An alternative to the use of FAAS, when the determination of a metal at the ultra trace level (µg kg-1) is desired, is the electrothermal atomic absorption spectrometry technique (ETAAS), in which a graphite oven substitutes the flame as atomization source. Generally the detection limit for ETAAS is three times lower than by flame atomization (Izário Filho, 1999). It is worth remembering that aside from the spectrometric techniques, it is possible to determine various metals (including Ni) by other methods. An example of a study in this sense was undertaken by Yang et al. (2005), who developed a method for determining Pb, Cd, Hg, Ni and Zn by high-efficiency liquid chromatography.

As important as the instrumentation is the pre-treatment stage of the sample. This stage is fundamental for reliable results, as well as optimization of the technique and method to be used, so as to reduce the time and cost of analyses, as well as to increase the degree of reliability of the results (Izário Filho, 1999). According to Wieteska et al. (1996) plant tissues are constantly used as bioindicators of the degree of pollution caused by a certain element to the environment. The introduction of new, ever-more effective techniques for the analysis of elements at trace levels which are simple and rapid comes to meet the growing need for control and monitoring of the disposal of inorganic compounds that cause harm to the environment and to human health (Ferreira et al., 2001). Along with the greater need for environmental control, the demand for legislation and inspection for analysis of trace elements also increases. In the case of Ni, the concern is pertinent since this element is mostly absorbed via food consumption, leading to harmful effects on human health (O'Neil et al., 2001; Wittsiepe et al., 2009; ATSDR, 2010).

The objectives of this study were to: (a) evaluate and optimize a method for preparation of vegetable tissue samples for Ni determination; (b) optimize the analytical procedures for determination by Flame Atomic Absorption Spectrometry (FAAS) and by Electrothermal Atomic Absorption (ETAAS) in vegetable samples and (c) determine Ni concentration in vegetables commonly consumed in the cities of Lorena and Taubaté in the Vale do Paraíba, state of São Paulo, Brazil.

Sample collection and preparation

Samples of lettuce, potato, beet, carrot and manioc were acquired on fruit and vegetable markets and from greengrocers four times in the period from August 2006 to March 2007 in the commercial area of two cities of the Vale do Paraíba, SP - Taubaté and Lorena. For each collection, two samples of each vegetable type were collected, one in each city. There was a total of 40 samples, eight samples of each type. For the tuberous vegetables, only roots and peels were acquired. In the case of leafy vegetables (lettuce), the leaves and stalk were acquired. All samples appeared suitable for human consumption and had no signs of rotting.

In the sample pretreatment, modified procedures for washing and drying proposed by Santos et al. (2004) and Kawashima & Soares (2003), respectively, were used. First, each plant sample was rinsed with distilled water to remove dirt and other debris. Then the vegetables were brushed with polypropylene bristles and washed with deionized water. The samples of the above-ground part of the lettuce were carefully cut with the stalks of each leaf, with the exception of the center stalk, which was discarded along with the roots. The samples of the underground parts of potato, beet, carrot and manioc were grated with a polypropylene grater into porcelain containers. Then the containers with the samples were dried in a laboratory oven at 65 ± 5 ºC for 24 h or until reaching constant weight. Immediately afterwards, the samples were stocked in polypropylene beakers and covered with a PVC film. Finally, they were stored in a desiccator. For moisture determination, a 1.0 ± 0.1 mg portion of the sample was used, according to the method described by Bianchi (1995). For each dehydrated sample analyzed, calculations were made to know how much of the weight of the corresponding fresh sample this sample represented (Equation 1):

where Mf represents the fresh sample mass (g), Ms the weighed dried sample mass (g) and Umid the mean moisture percentage of the sample. With the values of the FAAS and ETAAS analyses for Ni and Mf , the metal mass per fresh sample mass was calculated by equation 2:

in which m represents concentration of the metal per fresh sample mass (mg kg-1 or µg kg-1), C the metal concentration in the solution (mg L-1), Mf the fresh sample mass (g) and f the unit conversion factor (in this case, f = 1000).

Analyte dissolution

Nickel was determined using modified procedures of Wieteska et al. (1996) to prepare vegetable samples via acid digestion and calcination, for later determination by FAAS or ETAAS. Analyte addition and recovery tests were performed adding 1.5 mg of Ni standard to 0.5 g of dehydrated beet and manioc samples (equivalent to 30 mg kg-1 dry matter basis) for later determination in FAAS. In the dehydrated samples of lettuce, potatoes and carrots, 250 pg Ni was added to 0.5 g sample for the addition and recovery test by ETAAS (equivalent to 500 µg kg-1, dry matter basis).

CALCINATION: First, dehydrated samples of approximately 0.5 g of each plant were filled in porcelain crucibles and covered for calcination. The crucibles were transferred to a muffle furnace and exposed to a heating ramp (100 to 500 ºC) in temperature intervals of 100 ºC maintained for 20 min. Finally, the maximum temperature of 500 ºC was maintained for 2 h. The calcination residues were digested with 2.0 mL of deionized H2O, and 0.5 mL of HCl and 1.0 mL of HNO3, both concentrated. The crucibles were covered with watch glass and heated on a hotplate for 30 min, in a sand bath. This ensured a better control of heat and reflux, avoiding drift and evaporation loss completely, as well as the formation of metallic oxides of the elements of interest and ensuring complete digestion. After digestion and cooling, the entire digestion system was adequately rinsed with deionized water, the solutions of the crucibles were quantitatively transferred to 50.0 mL volumetric flasks and completed with deionized H2O.

ACID DIGESTION: 0.5 g of each dehydrated sample was filled in 50 mL glass beakers. Then, 5.0 mL of an acid mixture composed of HNO3 and HClO4 (4:1 v/v) and 2.0 mL of deionized H2O was pipetted into each beaker. Each beaker was covered with watch glass and transferred to a sand bath for a mild digestion, an important procedure when working with this type of acid mixture. Digestion time varied from 1 to 2 h, under continuous reflux of the solution of the system, to let the digestion product become as clear as possible (Wieteska et al., 1996). After digestion and cooling, the solutions of the crucibles were quantitatively transferred to 50.0 mL flasks and completed with deionized H2O.

The metal concentration in the plant samples was determined after dissolution using a Perkin-Elmer, model AAnalyst 800 atomic absorption spectrometer. The FAAS system with air/C2H2 flow was used to determine the metals in the samples of beets (Beta vulgaris L.), carrots (Daucus carota L. ) and manioc (Manihot utilissima L.) and ETAAS for the samples of lettuce (Lactuva sativa L. ) and potato (Solanum tuberosum L.). The experimental conditions are described in table 1.

 

 

Method optimization and validation

The method was optimized based on the pyrolysis and atomization curves for carrot samples, obtained according to the procedure described for analyte dissolution. For validation of the calcination and acid digestion methods, the addition and recovery test for the Ni was used in the vegetable tissue samples due to the nonexistence of certified standards for the vegetable tissues studied according to the National Institute of Standards and Technology - NIST, 110.4 Agricultural Materials, in powder form (NIST, 2006). In the validation, the characteristic mass value and experimental detection limit were considered.

The characteristic mass value (m0), which expresses the sensitivity of an analytical determination, is given by equation (3) (Izário Filho, 1999):

where the injected quantity is expressed in mL, the concentration in mg L-1 and the signal measured is the area under the curve.

Another procedure to express the sensitivity of an analytical determination is the value of the instrumental detection limit (IDL) of the elements in the diverse electrothermal systems. The IDL is defined by the baseline noise and the measurement sensitivity according to equation 4 (Izário Filho, 1999):

in which sbr is the standard deviation of the blank signal.

Nickel concentrations in vegetables consumed in Taubaté and Lorena

By the method optimized in this study (acid digestion), the Ni concentration in vegetable tissues commonly consumed in Taubaté and Lorena was determined using IBGE data from (IBGE, 2006), relating the metal concentration with the limits determined by Portaria 685 (Administrative Directive 685) of the Sanitary Inspection Office of the Ministry of Health (Secretaria de Vigilância Sanitária do Ministério da Saúde) as reported by Santos et al. (2004) (Table 2). The concentrations were determined for fresh matter, as foreseen in the above directive.

 

 

RESULTS AND DISCUSSION

Moisture of vegetable samples

The method used for determination of moisture proved to be viable since the repeatability was significant, ranging from 0.04 % for beet to 2.06 % for potato samples (Table 3). These experimentally obtained average moisture values were used for determination of the metal mass per fresh sample mass.

 

 

From the pyrolysis and atomization curves (Figure 1), it was possible to determine the best temperature related to these stages, ensuring a symmetric and representative atomization signal for the analyte mass. These data also permitted better programming for analysis via ETAAS. The characteristic mass (m0) values for calcination, calculated by equation (3), oscillated from 19.4 pg s-1 in carrot to 134.7 pg s-1 in potato samples. For the acid digestion method, m0 ranged from 37.3 pg s-1 in potato to 100.3 pg s-1 in carrot. Table 4 presents the optimized conditions for determination of Ni by ETAAS in terms of the digestion used.

 

 

 

 

The first tests evaluating calcination in the proposed period of 4 h were insufficient for a complete dry digestion of the manioc and beet samples. The ashes had to be digested with a mixture of HCl + HNO3 to ensure complete digestion of the matrix and solubilization of the analyte of interest. The need for a second digestion stage after calcination was observed by Wieteska et al. (1996) in the development of digestion procedures in an open system for lignocellulosic matrices. Even presenting a reasonable analytical frequency due to the 2nd digestion step, the calcination method proposed presents better analytical frequency than the dry digestion method proposed by Wieteska et al. (1996) and by Santos et al. (2004), who proposed a method for sample preparation via calcination for 24 h.

Regardless of the method, it was found that the instrumental limit (IDL) calculated by equation (4) varied from 1.7 to 8.1 pg. For the samples analyzed via FAAS, it was found that the experimental detection limit varied from 0.117 mg L-1 in manioc by acid digestion, to 0.152 mg L-1 in beet by the calcination method. The detection limit of the ETAAS technique was 0.140 µg L-1. It was observed that the procedures optimized for acid digestion were greater than the those optimized for calcination in most vegetables analyzed, possibly due to greater interference of the matrix with the chemical reagents.

Validation of the methods

After optimization of the procedures, Ni addition and recovery was tested with each sample type, also verifying the influence of the method used on the analyte recovery percentages. High recovery of the two Ni analysis methods by ETAAS and FAAS was observed, except in manioc samples by calcination (Table 5). The percentages of recovered analyte oscillated from 87.8 to 119.9 % by acid digestion and from 88.3 to 110.0 % by calcination, with the exception of Ni determination in manioc via calcination (64.8 %), possibly due to an incomplete digestion of this matrix. According to Krug & Nóbrega (Krug, 2008), a high residual C content, together with incomplete digestion of certain organic matrices, may lead to errors in precision and accuracy of the method chosen due to possible complexes formed between the analyte and the matrix. Consequently, the nonatomization of the analyte and effects of molecular absorption of the matriz during determination by spectrometric techniques due to incomplete digestion affect the results in terms of repeatability and reproducibility even more (Krug, 2008). With the exception of the manioc samples via calcination, the values may be considered analytically satisfactory for both methods, making an application of the method in the analytical Ni determinations viable in the samples of interest.

 

 

It is important to emphasize that this study does not intend to criticize other methods used for Ni analysis in vegetable samples, but simply to show that the methods tested are adequate for the quantification of this element. The tested methods represent an alternative procedure for laboratories where analytical determination methods of elements are required but there is a lack of automated sample digestion systems such as closed decomposition systems complemented by microwaves or of decomposition systems with focalized microwave radiation, in which the consumption of reagents may be more elevated than in the methods proposed in this study.

Nickel concentrations in the vegetables consumed in Taubaté and Lorena

For the analysis of real samples, a graph was drawn to compare the values obtained in the municipalities of Taubaté and Lorena. The Ni concentrations were reported in micrograms of the element per plant fresh matter (µg kg-1). The Ni contents in roots (potatoes and beets) of Lorena were of the same order of magnitude (50.5 ± 3.2 µg kg-1, 8.3 ± 1.2 mg kg-1, respectively) as in the samples from Taubaté (34.3 ± 5.5 µg kg-1, 9.9 ± 1.6 mg kg-1, respectively) (Table 6). In lettuce samples (103.0 ± 17.7 µg kg-1) Ni concentrations were around twice as high in samples from Taubaté than from Lorena (49.0 ± 6.1 µg kg-1). For carrot fresh matter, it was observed that concentrations in samples from Taubaté (230.0 ± 20.0 µg kg-1) were around 10 times higher than from Lorena (22.3 ± 5.0 µg kg-1).

 

 

In a comparison of the results (Table 6) with the legal tolerance limits (table 1), it was found that with exception of the carrot samples from Lorena, the levels exceeded the permitted. This was mainly true for the carrot samples in which Ni concentrations were more than five times greater than in samples from Taubaté. Some hypotheses may be suggested to explain this fact. It is possible that the means of contamination of the plants occurred through the air or the water used for the crops. It is also possible that the contamination was due to the use of urea fertilizers enriched with Ni to stimulate uptake by the vegetables (Dechen & Nachtigall, 2006). Another possibility would be the use of Ni-containing sewage sludge, which may have elevated Ni concentrations, as observed similarly by Revoredo & Melo (2006) in sorghum plants.

 

CONCLUSIONS

1. The analytical techniques for determination by ETAAS or FAAS could be validated by the analyte addition and recovery test. Both dry and wet digestion with HClO4-HNO3 proved to be viable for Ni quantification, serving as an alternative procedure in laboratories that need analytical methods for determination of elements and that lack automated sample digestion systems.

2. With the exception of carrot samples from Lorena, the Ni concentrations of all other plants investigated in this study exceeded the permitted by Brazilian legislation and.

3. The most alarming results, which call for more detailed studies, are the Ni concentrations in carrot samples from Taubaté, where levels were five times higher than determined by Brazilian regulations.

 

ACKNOWLEDGEMENTS

The authors gratefully acknowledge the financial support (Process no. 05/57382-6 and 05/53056-7) of the Research Support Foundation of the State of São Paulo (Fundação de Amparo à Pesquisa do Estado de São Paulo - FAPESP).

 

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Received for publication in March 2010 and approved in December 2010.

 

 

* Presented in two works on the XI Geochemistry Brazilian Congress. Granted by Fapesp (processes 57382-6 e 05/53056-7).

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