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Transfer of Cd, Pb, Ra and U from Phosphogypsum Amended Soils to Tomato Plants

机译:磷石膏改良土壤中镉,铅,镭和铀向番茄植物的转移

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About 170 million tons of phosphogypsum (PG) are annually generated worldwide as a by-product of phosphoric acid factories. Agricultural uses of PG could become the main sink for this waste, which usually contains significant radionuclide (from the 238U-series) and toxic metals concentrations. To study PG effects on pollutant uptake by crops, a completely randomised greenhouse experiment was carried out growing Lycopersicum esculentum Mill L. on a reclaimed marsh soil amended with three PG rates (treatments), corresponding to zero (control without PG application), one, three and ten times the typical PG rates used in SW Spain (20 Mg ha−1). The concentrations of Cd, Pb, U (by inductively coupled plasma mass spectroscopy) and 226Ra and 210Po (by γ-spectrometry and α-counting, respectively) were determined in soil, vegetal tissue and draining water. Cadmium concentrations in fruit increased with PG rates, reaching 44 ± 7 μg kg−1 formula weight with ten PG rates (being 50 μg kg−1 the maximum allowed concentration by EC 1881/2006 regulation). Cd transfer factors in non-edible parts were as high as 4.8 ± 0.5 (dry weight (d.w.)), two orders of magnitude higher than values found for lead, lead, uranium and radium concentrations in fruit remained below the corresponding detection limits—0.5 and 0.25 mg kg−1 and 0.6 mBq kg−1, respectively (in a d.w. basis). 238U (up to 7 μg kg−1 d.w.) and 210Po (up to 0.74 Bq kg−1 d.w.) could be measured in some fruit samples by α-spectrometry. Overall, the concentrations of these metals and radionuclides in the draining water accounted for less than 1% of the amount applied with PG.
机译:作为磷酸工厂的副产品,全世界每年生产约1.7亿吨磷石膏(PG)。 PG的农业用途可能成为这种废物的主要汇,通常含有大量的放射性核素(来自 238 U系列)和有毒金属。为了研究PG对农作物污染物吸收的影响,我们在改良的再生沼泽地上种植了番茄,番茄,Lycopersicum esculentum Mill L.,进行了完全随机的温室试验,修正了三种PG速率(处理),对应于零(未施用PG的对照),一种,是西班牙西南部典型PG率的三倍和十倍(20 Mg ha -1 )。测定Cd,Pb,U(通过电感耦合等离子体质谱法)和 226 Ra和 210 Po的浓度(分别通过γ光谱法和α计数法)在土壤,植物组织和排水中。水果中的镉浓度随着PG的增加而增加,达到10个PG的配方重量时达到44±7μgkg -1 配方重量(即EC允许的最大浓度50μgkg -1 1881/2006条)。不可食用部分中的Cd传递因子高达4.8±0.5(干重(dw)),比水果中铅,铅,铀和镭的浓度值高两个数量级,仍低于相应的检测极限-0.5分别为0.25 mg kg -1 和0.6 mBq kg -1 (以dw为基础)。 238 U(最高7μgkg −1 dw)和 210 Po(最高0.74 Bq kg −1 dw)可以通过α光谱法在一些水果样品中进行测量。总体而言,这些金属和放射性核素在排水中的浓度不到PG施用量的1%。

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