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Cadmium in upland forests after vitality fertilization with wood ash—a summary of soil microbiological studies into the potential risk of cadmium release

机译:用木灰进行活力施肥后山地森林中的镉-土壤微生物研究对镉释放潜在风险的概述

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摘要

The use of wood ash in forestry has been questioned because of the potential risk associated with its cadmium (Cd) content (1–30 mg kg−1). In agriculture, wood ash is only allowed for use as a fertilizer when its Cd content is below 3 mg kg−1. This restriction has not been applied to forest soils and there is a lack of knowledge about the potentially harmful effects of the Cd in wood ash on forest ecosystems. This paper summarizes our recent studies on the microbial communities of boreal coniferous forest humus exposed to Cd-containing wood ash treatment. The main objectives of our studies were to test if the Cd in wood ash has the potential to affect the humus layer microflora of coniferous upland forests and if it has the potential to enter the human food chain. These objectives were tested both in laboratory and field experiments with ash and ash spiked with Cd (in laboratory 400 or 1,000 mg Cd kg−1 as CdO or CdCl2; in field 400 mg Cd kg−1 as CdO). In one study the dissolution of ash was accelerated by irrigating it with simulated acid rain (SAR). Wood ash increased humus layer pH and microbial activities (respiration or thymidine incorporation rates) and changed its microfloral community structure (Biolog, PLFA, 16S or 18S rDNA PCR-DGGE) in both laboratory and field experiments. Spiking ash with Cd induced no further changes in the above-mentioned variables compared to ash alone. The Cd added with wood ash did not become bioavailable as detected with a bacterial biosensor Bacillus subtilis BR151(pTOO24). The form and level of Cd added in the ash had no further effect on the microbiological variables studied. Irrigation of ash with SAR did not increase the amount of bioavailable Cd, although the dissolution rate of the ash was increased. The concentration of Cd in soil water and in the berries of Vaccinium uliginosum and V. vitis-idaea, and the amount of humus bioavailable Cd did not increase with applied ash or ash spiked with Cd although the ash spiked with Cd increased the amount of humus total and extractable Cd in the 4-year field study. Only the ash spiked with Cd and not the unspiked “normal” wood ash resulted in significantly higher Cd concentrations in the mushroom Lactarius rufus and a slight increase in the berries of Empetrum nigrum (first year only). In conclusion, the Cd in wood ash did not become bioavailable and harmful to forest soil microbes, or leach into the humus layer even when treated with simulated acid rain. It is thus safe to use wood ash as a fertilizer in forests. However, since wood ash adds Cd to the environment, it is recommended that the same sites should not be fertilized with wood ash more than once. The effects of wood ash (3 t ha−1) on forest soil humus layer microbes are long-term, lasting at least 20 years, and probably longer if higher application dose and/or hardened ash is used.
机译:木材灰在林业中的使用受到质疑,因为其镉(Cd)含量(1–30 mg kg-1 )具有潜在的风险。在农业中,仅当Cd含量低于3 mg kg-1 时才允许使用木灰作为肥料。此限制尚未应用于森林土壤,并且缺乏关于木灰中Cd对森林生态系统的潜在有害影响的知识。本文总结了我们最近对含镉木灰处理的北方针叶林腐殖质微生物群落的研究。我们研究的主要目的是测试木灰中的镉是否有可能影响针叶高地森林的腐殖质层微生物区系,以及是否有可能进入人类食物链。这些目标在实验室和野外实验中均通过灰分和掺加Cd的灰分(实验室中400或1,000 mg Cd kg-1 作为CdO或CdCl2 ;在野外400 mg Cd kg-1 / sup>作为CdO)。在一项研究中,通过用模拟酸雨(SAR)灌溉灰分来加速灰分的溶解。在实验室和现场实验中,木灰均增加了腐殖质层的pH值和微生物活性(呼吸作用或胸苷掺入率),并改变了其微生物群落结构(Biolog,PLFA,16S或18S rDNA PCR-DGGE)。与单独的灰分相比,掺有Cd的灰分不会引起上述变量的进一步变化。如用细菌生物传感器枯草芽孢杆菌BR151(pTOO24)检测到的那样,添加了木灰的Cd不能生物利用。灰分中添加的镉的形式和含量对所研究的微生物变量没有进一步影响。尽管增加了灰分的溶解速度,但使用SAR灌溉灰分并没有增加生物利用Cd的量。施用的灰分或掺有Cd的灰分增加了腐殖质的含量,但土壤水和越橘和越桔的浆果中Cd的浓度以及腐殖质的生物利用Cd的量并未增加。四年实地研究中的总镉和可萃取镉。仅灰烬中掺有Cd的灰烬,而不掺入未掺入的“正常”木灰,会导致蘑菇菇中的Cd浓度显着升高,而Empetrum nigrum的浆果则略有增加(仅第一年)。总之,即使使用模拟酸雨处理,木灰中的Cd仍无法被生物利用并不会损害森林土壤微生物,也不会浸入腐殖质层。因此,在森林中使用木灰作为肥料是安全的。但是,由于木灰会向环境中添加Cd,因此建议在同一地点使用木灰施肥不要超过一次。木灰(3 t ha-1 )对森林土壤腐殖质层微生物的影响是长期的,至少持续20年,如果使用更高的施用剂量和/或硬化的灰分,则可能更长。

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