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烟秆炭修复重金属污染土壤的效应及对烟草生长的影响
引用本文:张建云,吴胜春,王敏艳,单胜道,曹志洪,张进.烟秆炭修复重金属污染土壤的效应及对烟草生长的影响[J].浙江农林大学学报,2018,35(4):674-683.
作者姓名:张建云  吴胜春  王敏艳  单胜道  曹志洪  张进
作者单位:1.浙江农林大学 环境与资源学院, 浙江 杭州 3113002.浙江农林大学 浙江省土壤污染生物修复重点实验室, 浙江 杭州 3113003.浙江农林大学 暨阳学院, 浙江 诸暨 3118004.浙江科技学院 生态环境研究院, 浙江 杭州 3100235.中国科学院 南京土壤研究所, 江苏 南京 210008
基金项目:浙江省重大科技专项重点农业项目2015C02037浙江省自然科学基金资助项目LQ17B070001浙江省科技厅公益技术研究项目2015C33050浙江省高等学校国内访问学者教师专业发展项目FX2015045
摘    要:为了评估烟秆炭修复重金属污染土壤上种植烟草Nicotiana tabacum的可行性,以烟秆炭作为土壤修复剂,以重金属污染土壤为研究对象,利用盆栽实验研究了不同烟秆炭施加量(0,20,40,80 g·kg-1)对重金属污染土壤肥力、重金属生物有效性、土壤酶活性指数及烟草产量、烟叶重金属质量分数的影响。结果表明:施用烟秆炭可以显著提高重金属污染土壤pH值、土壤肥力和土壤酶综合活性指数,显著降低污染土壤重金属生物有效性。与对照相比,添加80 g·kg-1的烟秆炭对土壤肥力的改善、酶活性指数的提升和对土壤中镉的钝化效果最好,土壤有机质和有效磷质量分数分别显著(P < 0.05)提高了2.0倍和3.4倍,土壤酶指数显著提升了24.8%;但施用施加40 g·kg-1的烟秆炭已能使铜、铅的钝化效果达到最佳,与对照相比分别显著(P < 0.05)下降了33.7%和29.5%。另一方面,施用烟秆炭能显著(P < 0.05)增加烟草有效叶数和叶片的宽度,烟叶鲜质量在炭施加量为40 g·kg-1时达到最高,比对照显著(P < 0.05)提高了近50.0%,同时烟叶中铜、镉质量分数降至最低。综合分析当烟秆炭施加量为土壤总质量的4%时,其对重金属污染土壤的修复效果最好。因此,利用烟秆制成的生物质炭修复重金属污染土壤种植烟草是可行的。

关 键 词:土壤学    生物质炭    烟秆炭    土壤修复    重金属生物有效性    氧化还原酶活性    烟草产量
收稿时间:2017-07-06

Tobacco stalk biochar in heavy metal contaminated soil amendments with tobacco production
ZHANG Jianyun,WU Shengchun,WANG Minyan,SHAN Shengdao,CAO Zhihong,ZHANG Jin.Tobacco stalk biochar in heavy metal contaminated soil amendments with tobacco production[J].Journal of Zhejiang A&F University,2018,35(4):674-683.
Authors:ZHANG Jianyun  WU Shengchun  WANG Minyan  SHAN Shengdao  CAO Zhihong  ZHANG Jin
Abstract:To assess the impacts of tobacco stalk biochar on tobacco (Nicotiana tabacum) growth and leaf yield, soil properties and metal immobilization in soil, and non-bioavailability to plants in a soil contaminated with Cu, Pb, and Cd, a pot experiment with biochar application rates of 0, 20, 40, and 80 g·kg-1 was conducted in Pingshan Experimental Ground in Zhejiang A&F University in 2016. And the biochar was mixed with 4 kg soil filled into plastic pots in a randomized design with 4 replications per treatment. Results compared to the control with no biochar additions, showed increases in soil pH, soil fertility, and soil enzyme activity indices as well as a decrease in soil heavy metal bioavailability with increasing application of biochar from 20 g·kg-1 to 80 g·kg-1. With a biochar application rate to the soil of 80 g·kg-1, content of soil organic matter and soil available P increased significantly (P < 0.05) (2.0 and 3.4 times, respectively), and the geometric mean of enzyme activities (GMea) also significantly increased (P < 0.05) (24.8%). Additionally, 40 g·kg-1 of biochar added to the soil led to the highest immobilization effect with decreases on Cu (33.7%) and Pb (29.5%) in the soil. Furthermore, with addition of biochar to the soil both number of tobacco leaves and foliar biomass increased significantly (P < 0.05). With a biochar application rate of 40 g·kg-1 to the soil, foliar fresh biomass was highest at nearly 50% higher than the control. At the same application rate of biochar to soil (40 g·kg-1), Cu and Cd concentrations in tobacco leaves significantly decreased (P < 0.05) to the lowest level. Thus, it may be feasible to use biochar derived from tobacco stalk waste to remediate metal-contaminated soils which can then be re-used for tobacco cultivation, and based on this study, 4% would be a suitable application rate for the biochar.
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