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首页> 外文期刊>Journal of Environmental Radioactivity >Fibre crops as alternative land use for radioactively contaminated arable land
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Fibre crops as alternative land use for radioactively contaminated arable land

机译:纤维作物作为放射性污染耕地的替代土地用途

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The transfer of radiocaesium, one of the most important and widespread contaminants following a nuclear accident, to the fibre crops hemp (Cannabis sativa L.) and flax (Linum usitatissimum L.) as well as the distribution of radiocaesium during crop conversion were studied for sandy soil under greenhouse and lysimeters conditions. Soil parameters did not unequivoqually explain the transfer factors (TF) observed. TFs to flax stems ranged from 1.34 to 2.80 X 10~(-3) m~2 kg~(-1). TFs to seeds are about a factor of 4 lower. During the retting process for separating the fibres from the straw, more than 95% of the activity was removed with the retting water. For hemp, the TF to the stem was about 0.6 X 10~(-3) m~2 kg~(-1). For hemp, straw and fibres were mechanically separated and TF to straw was about 0.5 X 10m~2 kg~(-1) and to fibres 1.0 X 10m~2 kg~(-1). Generally, the TFs to the useable plant parts both for hemp and flax, are low enough to allow for the production of clean end-products (fibre, seed oil, biofuel) even on heavily contaminated land. Given the considerable decontamination during retting, contamination levels in flax fibres would only exceed the exemption limits for fibre use after production in extreme contamination scenarios ( > 12 300 kBq m~(-2)). Since hemp fibres are mechanically separated, use of hemp fibres is more restricted (contamination < 740 kBq m~(-2)). Use of stems as biofuel is restricted to areas with contamination levels of < 250 and 1050 kBq m~(-2) for flax and hemp, respectively. Use of seeds for edible oil production and flour is possible almost without restriction for flax but due to the high TFs to seed observed for hemp (up to 3 X 10m~2 kg~(-1)) consumption of hemp seed products should be considered with care.
机译:研究了核事故后最重要和最广泛的污染物之一放射性铯向纤维作物的大麻(Cannabis sativa L.)和亚麻(Linum usitatissimum L.)的转移以及作物转化过程中放射性铯的分布。温室和溶度计条件下的沙质土壤。土壤参数并不能明确解释观察到的传递因子(TF)。亚麻茎的TFs范围为1.34至2.80 X 10〜(-3)m〜2 kg〜(-1)。种子的TF大约低4倍。在用于将纤维与稻草分离的浸胶过程中,用浸胶水除去了超过95%的活性。对于大麻,茎的TF约为0.6 X 10〜(-3)m〜2 kg〜(-1)。对于大麻,机械地分离秸秆和纤维,对秸秆的TF约为0.5 X 10m〜2 kg〜(-1),对纤维的TF为1.0 X 10m〜2 kg〜(-1)。通常,用于大麻和亚麻的植物可用部分的TFs足够低,即使在污染严重的土地上也可以生产清洁的最终产品(纤维,种子油,生物燃料)。考虑到脱胶过程中的大量去污,亚麻纤维中的污染水平仅会超过在极端污染情况下(> 12 300 kBq m〜(-2))生产后使用的纤维的豁免限值。由于大麻纤维是机械分离的,因此大麻纤维的使用受到更多限制(污染<740 kBq m〜(-2))。只能将茎用作生物燃料的地区仅限于亚麻和大麻的污染水平分别<250和1050 kBq m〜(-2)。可以将种子用于食用油生产和面粉,几乎不受亚麻的限制,但是由于大麻中种子的TF较高(高达3 X 10m〜2 kg〜(-1)),因此应考虑食用大麻种子产品小心。

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