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Extraction with hot water is the most widely used procedure to determine boron (B) in soils for the diagnosis of the nutrient availability for plants. However, this procedure is tedious for routine conditions and requires some special precautions. An alternative extraction procedure was developed, consisting in the extraction of B with a 1.25 g/L solution of barium chloride (BaCl 2 ) or with water heated in a domestic microwave oven. Boron was determined either by inductively coupled argon plasma emission spectrometry (ICP-AES) and by spectrophotometry with azomethine-H. Good correlations were found between the extraction by boiling water under reflux and the extraction by the microwave heating for 13 Brazilian soils, and the contents of B obtained by spectrophotometry did not differ significantly from those obtained by ICP-AES. Considering the calculated standard deviations, it can be concluded that microwave heating followed by ICP-AES determination is an adequate procedure for the determination of hot water extractable B in soils.

Accumulation of heavy metals in unconsolidated soils can prove toxic to proximal environments, if measures are not taken to stabilize soils. One way to minimize the toxicity of metals in soils is the use of materials capable of immobilizing these contaminants by sorption. Biochar (BC) can retain large amounts of heavy metals due to, among other characteristics, its large surface area. In the current experiment, sugarcane-straw-derived biochar, produced at 700 °C, was applied to a heavy-metal-contaminated mine soil at 1.5, 3.0, and 5.0% (w/w). Jack bean and Mucuna aterrima were grown in pots containing a mine contaminated soil and soil mixed with BC. Pore water was sampled to assess the effects of biochar on zinc solubility, while soils were analyzed by DTPA extraction to confirm available metal concentrations. The application of BC decreased the available concentrations of Cd, Pb, and Zn in the mine contaminated soil leading to a consistent reduction in the concentration of Zn in the pore water. Amendment with BC reduced plant uptake of Cd, Pb, and Zn with the jack bean uptaking higher amounts of Cd and Pb than M. aterrima. This study indicates that biochar application during mine soil remediation could reduce plant concentrations of heavy metals. Coupled with this, symptoms of heavy metal toxicity were absent only in plants growing in pots amended with biochar. The reduction in metal bioavailability and other modifications to the substrate induced by the application of biochar may be beneficial to the establishment of a green cover on top of mine soil to aid remediation and reduce risks.

Microelements are an important issue in agriculture, due to their need as micronutrients for plants and also to the possibility of the build-up of toxic levels for plants and animals. Five micronutrients (B, Cu, Fe, Mn, and Zn) are routinely determined in soil analysis for advisory purposes. Other four elements (Cd, Cr, Pb, and Ni) are considered environmentally important heavy metals in farmland soils. Thus high contents of these metals in cropland might go eventually unnoticed. In this paper we present an approach that can be used to monitor the contents of the nine elements in farmland soils using advisory soil testing. A total of 13,416 soil samples from 21 Brazilian states, 58% of them from the state of São Paulo, sent by farmers were analyzed. Boron was determined by hot water extraction and the other metals were determined by DTPA (pH 7.3) extraction. The ranges of content, given in mg dm -3 soil, were the following: B, 0.01-10.6; Cu, 0.1-56.2; Fe, 0.5-476; Mn, 1-325; Zn, 1-453; Cd, 0.00-3.43, Cr, 0.00-42.9; Ni, 0.00-65.1; Pb, 0.00-63.9. The respective average values for São Paulo were: B-0.32; Cu-2.5; Fe-36; Mn-16; Zn-4.8; Cd-0.02; Cr-0.03; Ni-0.18; Pb-0.85. For other states the results are in the same ranges. The higher values are indicative of anthropogenic inputs, either due to excess application of fertilizers or to industrial or mining activities. The conclusion is that massive chemical analysis of farmland soil samples could serve as a database for indicating potential micronutrient deficiency and excesses or heavy metal buil-up in croplands, allowing preventive actions to be taken. Key words: soil analyses, micronutrients, heavy metals, deficiency, toxicity, interpretation limits USO DA ANÁLISE DE ROTINA PARA MONITORAR A CONCENTRAÇÃO DE METAIS PESADOS E BORO EM SOLOSRESUMO: Microelementos têm um papel importante na agricultura, devido à sua essencialidade para plantas e também à possibilidade de serem tóxicos às plantas e aos animais. Os cinco micronutrientes (B, Cu, Fe, Mn, e Zn) são comumente determinados nas análises rotineiras de solos com finalidade de recomendação de adubação. Os outros quatro elementos (Cd, Cr, Pb, e Ni) são metais pesados importantes para os solos agrícolas e não são normalmente determinados em amostras de solos enviadas pelos agricultores. Portanto, altos teores desses metais pesados em terras agricultáveis poderão passar despercebidos. O objetivo deste trabalho foi usar a análise de rotina de solo para monitorar o teor dos nove elementos em amostras de solo. Um total de 13.416 amostras de solo de 21 estados brasileiros, sendo 58% delas originárias do estado de São Paulo, foram analisadas. O boro foi determinado usando a água quente e os outros metais foram extraídos pelo DTPA (pH 7,3). Considerando todas as amostras, as faixas dos teores, em de mg dm -3 foram:

The aim of the paper was to contribute to the acquisition of background data for the specification of safe boron levels in soils in relation to diagnostics by multi-nutrient soil tests and to CEC (cation exchange capacity) value of soil, pH and soil organic matter. The research was conducted on 24 soils. Sorption was determined after 97 days from the application of B at the rates of 0, 1, 2.5, 5 mg B/kg in H 3 BO 3. The closest regression of B-sorption was with the CEC value of soil in NH 4-acetate and water tests and it increased with the increasing application of B (regressi-on at a rate of 5 ppm B; NH 4-acetate: linear R 2 = 0.632, polynomial 2 nd R 2 = 0.644; water: linear R 2 = 0.644, polynomial 2 nd R 2 = 0.599). No relationship was found in the Mehlich 3 test. Regressions of B sorption on pH value were substantially lower. The relationship of B sorption with soil organic matter was similar to CEC, but less close. In the NH 4-acetate soil test, after the correction of CEC value of soil by pH deviations from the optimum, regression was improved (linear R 2 = 0.821, polynomial 2 nd R 2 = 0.837).