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纳米氧化铜颗粒对玉米和微生物群落的毒性在很大程度上取决于其生物可利用分数。

Toxicity of nano-CuO particles to maize and microbial community largely depends on its bioavailable fractions.

机构信息

State Key Laboratory of Geohazard Prevention and Geoenvironment Protection (Chengdu University of Technology), 1# Dongsanlu, Erxianqiao, Chengdu 610059, Sichuan, P.R. China; State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, P.R. China.

State Key Laboratory of Geohazard Prevention and Geoenvironment Protection (Chengdu University of Technology), 1# Dongsanlu, Erxianqiao, Chengdu 610059, Sichuan, P.R. China.

出版信息

Environ Pollut. 2019 Dec;255(Pt 2):113248. doi: 10.1016/j.envpol.2019.113248. Epub 2019 Sep 17.

Abstract

The environmental consequences of nano-CuO particles have gained significant attention in recent decades. Identification of the mechanisms for soil and plant responses with respect to the chemical speciation of nano-CuO (mainly the exchangeable and reducible fractions) remains scarce. Here, we analyzed different chemical speciation of Cu and DTPA-extractable Cu over 42 days in (1) control soil without Cu addition; (2) soil treated with nano-CuO particles; and (3) soil treated with CuSO solution. The applied dose was 500 mg Cu kg and maize was grown in these soils. Plant growth was inhibited, but the inhibition by nano-CuO was slightly weaker compared to CuSO. Cu accumulations were similar in the roots for CuSO and nano-CuO treatments, but significantly higher in the shoots for CuSO treatment. This indicates that Cu from nano-CuO-treated soils mainly accumulated in roots but rarely transferred to shoots. Enzyme activities on the rhizoplane visualized by zymography were strongly depressed by CuSO but slightly inhibited by nano-CuO. Microbial community diversity measured by 16S rRNA was the lowest in CuSO-treated soils among three treatments. These results were explained by the following mechanisms: (1) Gradual increases of DTPA-extractable and exchangeable Cu were found in nano-CuO-treated soil, and the final concentrations at day 42 were only half of those in CuSO-treated soil; (2) Enzyme activities on the rhizoplane were positively related to soil pH and negatively correlated with DTPA-extractable and exchangeable Cu; (3) Even though reducible Cu in nano-CuO-treated soils was 1.3 times higher than in CuSO-treated soils, indicating stronger nano-accrued oxidative stress in nano-CuO-treated soils, the toxicity induced by nano-CuO particles was still weaker than CuSO. Nevertheless, the toxicity of Cu particles to plants and microbes mainly depends on the gradually-released bioavailable Cu. This demonstrates the greater importance of bioavailable Cu concentrations for toxicity modulation rather than the scale of Cu particles.

摘要

纳米氧化铜颗粒对环境的影响近年来受到了广泛关注。对于纳米氧化铜(主要是可交换态和还原态)的化学形态,识别土壤和植物响应的机制仍然很少。在这里,我们分析了在(1)不添加铜的对照土壤;(2)用纳米氧化铜颗粒处理的土壤;(3)用 CuSO 溶液处理的土壤中,42 天内不同的铜化学形态和 DTPA 可提取铜的变化。应用剂量为 500mg Cu kg,在这些土壤中种植玉米。植物生长受到抑制,但纳米氧化铜的抑制作用略弱于 CuSO。CuSO 和纳米氧化铜处理的根中 Cu 积累相似,但 CuSO 处理的地上部 Cu 积累明显更高。这表明来自纳米氧化铜处理土壤的 Cu 主要积累在根部,但很少转移到地上部。通过同工酶图谱在根际表面观察到的酶活性被 CuSO 强烈抑制,但被纳米氧化铜轻微抑制。三种处理中,CuSO 处理的土壤中 16S rRNA 测量的微生物群落多样性最低。这些结果可以通过以下机制来解释:(1)在纳米氧化铜处理的土壤中,DTPA 可提取和可交换铜逐渐增加,第 42 天的最终浓度仅为 CuSO 处理土壤的一半;(2)根际表面的酶活性与土壤 pH 呈正相关,与 DTPA 可提取和可交换铜呈负相关;(3)尽管纳米氧化铜处理土壤中的可还原铜比 CuSO 处理土壤高 1.3 倍,表明纳米氧化铜处理土壤中纳米氧化铜积累的氧化应激更强,但纳米氧化铜颗粒的毒性仍弱于 CuSO。然而,Cu 颗粒对植物和微生物的毒性主要取决于逐渐释放的生物可利用 Cu。这表明生物可利用 Cu 浓度对毒性调节的重要性大于 Cu 颗粒的大小。

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