设施菜田土壤氮磷淋失对镁改性生物炭施用的响应OA
Response of nitrogen and phosphorus leaching in greenhouse vegetable soils to magnesium-modified biochar application
为解决设施菜田土壤因氮、磷过量累积引发的淋失污染问题,本研究以玉米秸秆和竹子为原料,在550℃条件下制备未改性生物炭(MB和BB)及镁改性生物炭(Mg-MB和Mg-BB),通过吸附试验、土柱淋溶试验,并结合扫描电镜-能谱、傅里叶变换红外光谱表征手段,探究镁改性生物炭对氮、磷共存的吸附性能及设施土壤氮、磷淋失的阻控效果.结果显示,镁改性未破坏生物炭碳架结构,表面新增Mg—O键(620 cm-1)且含氧官能团(—OH、—COOH)强度增强.吸附试验表明,生物炭(除BB处理外)对氮、磷吸附符合Langmuir模型,且拟二级动力学模型拟合度更优,吸附以单层均匀化学吸附为主;镁改性后生物炭对NO3-的最大理论吸附量均提升,其中Mg-MB、Mg-BB处理较对应的MB、BB处理分别增加81.18%和7.77%,且Mg-BB处理吸附量最大;Mg-MB、Mg-BB处理对PO43-的最大理论吸附量分别是对应MB、BB处理的1.21和2.09倍,且Mg-MB、MB处理对磷的吸附量均高于Mg-BB、BB处理.土柱淋溶试验中,所有生物炭处理土壤氮、磷淋失量较不加生物炭显著降低,其中Mg-BB处理阻控氮淋失效果最佳(降幅44.36%),Mg-MB处理阻控磷淋失效果最佳(降幅21.52%);镁改性生物炭较对应未改性生物炭氮、磷淋失量更低,且Mg-BB较BB处理淋溶液可溶性无机氮、可溶性有机氮和硝态氮占比分别显著降低17.24%、10.61%和12.88%,Mg-MB较MB处理淋溶液可溶性反应磷和可溶性有机磷占比分别降低6.81%和3.66%.综上,镁改性可提升生物炭对共存氮、磷的吸附能力,且原料存在功能分化,Mg-BB更适用于氮素淋失阻控,Mg-MB更适用于磷素淋失阻控,可为设施菜田土壤养分管理及环境风险防控提供针对性材料选择依据.
To address leaching pollution from excessive nitrogen(N)and phosphorus(P)accumulation in greenhouse vegetable soil,this study prepared unmodified biochars(MB from corn stover,BB from bamboo)and Mg-modified biochars(Mg-MB,Mg-BB)at 550 ℃.Batch adsorption experiments,soil column leaching experiments,and characterizations(Scanning electron microscope-energy dispersive spectroscppy,Fourier transform infrared spectroscopy)were conducted to explore the adsorption performance of Mg-modified biochars for coexisting N and P,and their mitigation effect on N and P leaching in greenhouse vegetable soil.Results showed that Mg modification did not destroy the biochar carbon skeleton,but introduced Mg—O bonds(620 cm-1)and enhanced the intensity of oxygen-containing functional groups(—OH,—COOH).Adsorption experiments indicated that all biochars except BB treatment fitted the Langmuir model,with better fitting to the pseudo-second-order kinetic model,suggesting monolayer homogeneous chemisorption as the dominant mechanism.Mg modification increased the maximum theoretical adsorption capacity of biochars for NO3-:Mg-MB and Mg-BB treatments increased by 81.18%and 7.77%,compared with MB and BB treatments,respectively,with Mg-BB treatment showing the highest NO3-adsorption.For PO43-,the maximum adsorption capacities of Mg-MB and Mg-BB treatments were 1.21 and 2.09 times those of MB and BB treatments,respectively,while MB and Mg-MB treatments had higher P adsorption than BB and Mg-BB treatments.In soil column leaching experiments,all biochar treatments significantly reduced N and P leaching compared to treatment without biochar:Mg-BB treatment had the best N leaching mitigation(44.36%reduction),and Mg-MB treatment had the best P leaching mitigation(21.52%reduction).Mg-modified biochars showed lower N and P leaching than their unmodified biochars.Specifically,Mg-BB treatment significantly reduced the proportions of dissolved inorganic nitrogen,dissolved organic nitrogen,and nitrate nitrogen in leachate by 17.24%,10.61%,and 12.88%,compared with BB treatment;Mg-MB treatment reduced the proportions of soluble reactive phosphorus and soluble organic phosphorus by 6.81%and 3.66%,compared with MB treatment.In conclusion,Mg modification enhances adsorption capacity of biochars for coexisting N and P,with feedstock-dependent functional differentiation:Mg-BB treatment is more suitable for N leaching mitigation,while Mg-MB treatment is better for P leaching mitigation.This provided a basis for targeted material selection in nutrient management and environmental risk control of greenhouse vegetable soil.
王亚玲;成宇阳;王赫;彭正萍;梅秀文;文新月;刘春敬;王秀斌
河北农业大学资源与环境科学学院,河北 保定 071000||北方干旱半干旱耕地高效利用全国重点实验室/中国农业科学院农业资源与农业区划研究所,北京 100081北方干旱半干旱耕地高效利用全国重点实验室/中国农业科学院农业资源与农业区划研究所,北京 100081河北农业大学资源与环境科学学院,河北 保定 071000河北农业大学资源与环境科学学院,河北 保定 071000北方干旱半干旱耕地高效利用全国重点实验室/中国农业科学院农业资源与农业区划研究所,北京 100081北方干旱半干旱耕地高效利用全国重点实验室/中国农业科学院农业资源与农业区划研究所,北京 100081河北农业大学资源与环境科学学院,河北 保定 071000北方干旱半干旱耕地高效利用全国重点实验室/中国农业科学院农业资源与农业区划研究所,北京 100081
镁改性生物炭氮、磷吸附氮、磷淋失设施菜田土壤
Mg-modified biocharnitrogen and phosphorus adsorptionnitrogen and phosphorus leachinggreenhouse vegetable soils
《中国土壤与肥料》 2026 (4)
1-11,11
国家自然科学基金项目(2272816).
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