范峰华,郑荣波,郭雪莲,方昕,付倩,刘爽.二氧化钛纳米颗粒对湖滨沼泽土壤氮矿化的影响[J].环境科学学报,2020,40(6):2220-2228
二氧化钛纳米颗粒对湖滨沼泽土壤氮矿化的影响
- Effects of TiO2 nanoparticles on the mineralization of soil nitrogen in a lakeshore marsh
- 基金项目:国家自然科学基金项目(41563008);云南省高原湿地科学创新团队(2012HC007)
- 范峰华
- 1. 西南林业大学湿地学院, 昆明 650224;2. 国家高原湿地研究中心, 昆明 650224
- 郑荣波
- 西南林业大学化学工程学院, 昆明 650224
- 郭雪莲
- 1. 西南林业大学湿地学院, 昆明 650224;2. 国家高原湿地研究中心, 昆明 650224
- 方昕
- 1. 西南林业大学湿地学院, 昆明 650224;2. 国家高原湿地研究中心, 昆明 650224
- 付倩
- 1. 西南林业大学湿地学院, 昆明 650224;2. 国家高原湿地研究中心, 昆明 650224
- 刘爽
- 1. 西南林业大学湿地学院, 昆明 650224;2. 国家高原湿地研究中心, 昆明 650224
- 摘要:二氧化钛纳米颗粒(TiO2NPs)的广泛应用使其环境释放量不断增加,从而影响到土壤氮的转化过程.然而,目前关于TiO2NPs对湖滨沼泽土壤氮矿化的影响机制尚不明确.因此,本研究以典型沼泽土壤为研究对象,通过室内培养实验研究不同剂量TiO2NPs处理(0 mg·kg-1(CK)、10 mg·kg-1(A10)、100 mg·kg-1(A100)、250 mg·kg-1(A250)、1000 mg·kg-1(A1000))对土壤理化性质、酶活性和氮矿化过程的影响,探讨TiO2NPs输入对土壤氮矿化过程影响的内在机制.结果表明:①不同剂量TiO2NPs处理显著降低了土壤pH和总有机碳(TOC)含量(p<0.05),A100、A250和A1000处理显著降低了硝态氮(NO3--N)含量(p<0.05).②A250和A1000处理显著抑制了过氧化氢酶活性(p<0.05);培养7 d,不同剂量TiO2NPs处理均显著促进了脲酶活性(p<0.05),抑制了脱氢酶活性(p<0.05);随着培养时间延长,TiO2NPs处理对脲酶和脱氢酶活性的抑制作用逐渐减弱,表明TiO2NPs的负面作用会随时间减弱.③不同剂量TiO2NPs处理对氨化速率没有显著影响(p>0.05),A250、A1000处理对硝化和矿化速率有显著抑制作用(p<0.01).④土壤氮矿化速率与土壤pH、总磷(TP)、NO3--N含量呈显著正相关,与脲酶、过氧化氢酶活性呈显著负相关.TiO2NPs主要通过改变沼泽土壤NO3--N含量影响氮矿化过程.本研究可为湖滨湿地保护和TiO2NPs环境风险评估提供理论依据.
- Abstract:The wide spread use of TiO2 nanoparticles (TiO2NPs) is increasing their environmental release, which could change the process of soil nitrogen transformation. However, the mechanism of the effect of TiO2NPs input on the mineralization of soil nitrogen in lakeshore marshes is still unclear. In order to explore the effects and the mechanism of TiO2NPs input on soil nitrogen mineralization, the soil was collected from a lakeshore marsh field and an indoor cultivated experiment with different addition of TiO2NPs was conducted. The amount of TiO2NPs was added with 0 mg·kg-1(CK), 10 mg·kg-1(A10), 100 mg·kg-1(A100), 250 mg·kg-1(A250) and 1000 mg·kg-1 (A1000), respectively. The soil physiochemical properties, enzyme activities and nitrogen mineralization rate of marsh soil were tested for each treatment. The results showed that ① all TiO2NPs addition significantly reduced soil pH and total organic carbon (TOC) (p<0.05). The treatments of A100, A250 and A1000 significantly reduced the content of soil nitrate (NO3--N) (p<0.05). ② The treatments of A250 and A1000 significantly reduced the activity of catalase (p<0.05). All TiO2NPs addition significantly promoted the activity of urease, but reduced the activity of dehydrogenase after seven days cultivation. With the prolonged period of cultivation, the inhibition of TiO2NPs on the activity of urease and dehydrogenase decreased gradually, which means that the negative effect of TiO2NPs on enzyme activity would fade with time. ③ Treatments with TiO2NPs addition did not significantly affect soil ammonization rate (p>0.05), while the treatments of A250 and A1000 significantly reduced soil nitrification rate and mineralization rate (p<0.01). ④ Soil nitrogen mineralization rate positively correlated with soil pH, total phosphorus (TP) and NO3--N contents, but negatively correlated with the activity of catalase and urease. TiO2NPs addition changed the mineralization process of soil nitrogen by regulating the content of NO3--N in lakeshore marshes. This study provides a theoretical basis for the protection of lakeshore marshes and the assessment of TiO2NPs environmental risks.