1. 吉林农业大学资源与环境学院, 农业农村部盐碱土改良与利用(东北内陆盐碱地)重点实验室,长春,130118
2. 临沂市生态环境局临沭县分局, 山东 临沭,276700
[ "郑玉昕(1999—),女,在读硕士研究生,主要从事土壤中污染物的迁移和转化研究。E-mail:zhengyuxin9@163.com" ]
纸质出版:2023
移动端阅览
郑玉昕, 赵兴敏, 朱孟龙, 等. 种稻配施改良剂对苏打盐碱土—水—作物系统氟迁移的影响[J]. 水土保持学报, 2023,37(2):385-391.
ZHENG Yuxin, ZHAO Xingmin, ZHU Menglong, et al. Effects of Rice Planting with Amendments on Fluorine Migration in Soda Saline-Alkali Soil-Water-Crop System[J]. 2023, 37(2): 385-391.
郑玉昕, 赵兴敏, 朱孟龙, 等. 种稻配施改良剂对苏打盐碱土—水—作物系统氟迁移的影响[J]. 水土保持学报, 2023,37(2):385-391. DOI: 10.13870/j.cnki.stbcxb.2023.02.045.
ZHENG Yuxin, ZHAO Xingmin, ZHU Menglong, et al. Effects of Rice Planting with Amendments on Fluorine Migration in Soda Saline-Alkali Soil-Water-Crop System[J]. 2023, 37(2): 385-391. DOI: 10.13870/j.cnki.stbcxb.2023.02.045.
为探讨化学改良剂对苏打盐碱土稻田生态系统中氟迁移的影响
采用盆栽试验
研究硫酸铝、脱硫石膏和有机复合改良剂作用下的土壤各形态氟含量变化
以及土壤氟向水体和地上部植株的迁移情况。结果表明
化学改良剂影响苏打盐碱土—水—作物系统中氟的迁移及生物有效性。种稻后各改良剂处理的土壤水溶态氟变化范围为8.33~20.90 mg/kg
与对照相比
均呈下降趋势
其中硫酸铝处理下降得最多
降低60.15%;可交换态氟和有机束缚态氟呈增加趋势
其中有机复合改良剂处理增加得最多
分别为79.54%和86.37%;种稻前后铁锰氧化物结合态氟变化较复杂
其中硫酸铝处理无显著变化
对照处理和有机复合改良剂处理分别增加19.05%和42.03%
而脱硫石膏处理下降22.79%;残余态氟和总氟含量呈下降趋势
其中有机复合改良剂处理的残余态氟降低得最多
为35.50%
硫酸铝处理的总氟降低得最少
为10.47%
其余处理降幅为12.50%~12.55%。在水稻种植过程中
土壤中氟向水中累积释放总量为对照>有机复合改良剂>脱硫石膏>硫酸铝
与对照相比
其他3个处理分别降低3.25%
5.13%和5.19%。土壤中氟向水稻茎叶和稻谷的迁移总量依次为有机复合改良剂>脱硫石膏>硫酸铝
单位土壤的迁移量分别为0.44
0.40
0.25 mg/kg
迁移率分别为0.16%
0.15%和0.09%。相关分析表明
土壤中氟向水中释放总量和向水稻茎叶迁移总量均与土壤pH、可溶盐和各形态氟含量呈显著的正相关关系
而水稻稻谷的含氟量不受土壤性质影响。由于硫酸铝处理的水稻茎叶对氟的吸收量显著低于其他处理
并且土壤水溶态氟含量及土壤向水中释放的氟总量也较少
所以硫酸铝改良剂具有较好地降低苏打盐碱稻田土氟迁移和生物有效性的能力。
In order to study the effect of chemical amendments on fluorine migration in the paddy ecosystem of soda saline-alkali soil
pot experiments were conducted to study the changes of fluorine content in various forms of soil and the migration of soil fluorine to water and aboveground plants under the effects of aluminum sulfate
desulfurized gypsum and organic compound modifiers.The results showed that chemical amendments would affect the migration and bioavailability of fluorine in soda saline-alkali soil-water-crop system.After planting rice
the variation of soil water-soluble fluorine in each amendment treatment ranged from 8.33 to 20.90 mg/kg
which showed a downward trend compared with the control
of which aluminum sulfate treatment decreased the most
by 60.15%;Exchangeable fluorine and organic bound fluorine showed an increasing trend
among which the organic compound modifier treatment increased the most
by 79.54% and 86.37% respectively;The changes of iron manganese oxide bound fluorine before and after rice planting were complex
among which aluminum sulfate treatment had no significant change
the control treatment and organic compound modifier treatment increased by 19.05% and 42.03% respectively
while desulfurization gypsum treatment decreased by 22.79%;The contents of residual fluorine and total fluorine showed a downward trend
among which the residual fluorine decreased the most by 35.50% under the organic compound modifier treatment
the total fluorine decreased the least by 10.47% under the aluminum sulfate treatment
and the other treatments decreased by 12.50% to 12.55%.In the process of rice planting
the total cumulative released amount of fluorine from soil to water was control > organic compound modifier > desulfurization gypsum > aluminum sulfate.Compared with the control
the other three treatments decreased by 3.25%
5.13% and 5.19% respectively.The total migration amount of fluorine in soil migrating to rice stems
leaves and paddy was in the order of organic compound modifier > desulfurized gypsum > aluminum sulfate
the migration amount per unit soil was 0.44
0.40 and 0.25 mg/kg respectively
and the migration rates were 0.16%
0.15% and 0.09% respectively.The results of correlation analysis showed that the total amount of fluorine released from soil to water and transferred to rice stems and leaves in soil were positively correlated with soil pH
soluble salt and various forms of fluorine content
while the fluorine content of rice paddy was not affected by soil properties.Because the absorption of fluorine by rice stems and leaves under the aluminum sulfate treatment was significantly lower than that of other treatments
and the content of water-soluble fluorine in soil and the total amount of fluorine released from soil to water were also less
aluminum sulfate modifier had a better ability to reduce fluorine migration and bioavailability in soda saline-alkali paddy soil.
林英姿,刘莞青,王高琪,等.吉林西部含氟盐碱地改良研究现状[J].农业与技术,2021,41(8):899-900,8101.
赵兰坡,尚庆昌,李春林.松辽平原苏打盐碱土改良利用研究现状及问题[J].吉林农业大学学报,2000,22(专辑):79-83,85.
刘金华,王玉军,杨靖民,等.吉林省西部氟病区苏打盐碱土氟的赋存形态及分布特征[J].土壤,2017,49(3):558-564.
Cai H, Guo C L, Zhang M G, et al. Fluoring content in soil and groundwater of Songnen Plain in northeast China[J].Agricultural Science and Technology,2013,14(2):376-383.
刘金华.苏打盐碱土氟分布及铝氟互作效应研究[D].长春:吉林农业大学,2013.
Perrot K W. The reaction of fluoride with soil and soil mineral[J].Soil Science,1976,27:58-76.
吴卫红,谢正苗,徐建明,等.不同土壤中氟赋存形态特征及其影响因素[J].环境科学,2002,23(2):104-108.
杨金燕,苟敏.中国土壤氟污染研究现状[J].生态环境学报,2017,26(3):506-513.
刘璇,梁秀娟,肖霄,等.pH对吉林西部湖泊底泥中不同形态氟迁移转化影响的实验研究[J].环境污染与防治, 2011,33(6):19-22.
张璐,黄立华.淹水在苏打盐碱土形成过程中的作用:苏打盐碱土形成原因的探讨[J].土壤与作物,2018,7(4):365-373.
张梅.吉林省西部苏打盐碱土种稻改良机理与生产关键技术研究[D].长春:吉林农业大学,2015.
于群英,李孝良,汪建飞,等.安徽省土壤氟含量及其赋存特征[J].长江流域资源与环境,2013,22(7):915-921.
国家环境保护局,中国环境监测总站.中国土壤元素背景值[M].北京:中国环境科学出版社,1990.
国家环境保护局科技标准司.土壤环境质量标准GB 15618—1995[S].北京:中国环境科学出版社,1995.
王宇,韩兴,赵兰坡. 硫酸铝对苏打盐碱土的改良作用研究[J].水土保持学报,2006,20(4):50-53.
Fuge R. Fluorine in the environment,a review of its sources and geochemistry[J].Applied Geochemistry,2019,100:393-406.
Lv L, He J, Wei M, et al. Factors influencing the removal of fluoride from aqueous solution by calcined Mg-Al-CO
3
layered double hydroxides[J].Journal of Hazardous Materials,2006,133(1/3):119-128.
赵兰坡,王宇,马晶,等.吉林省西部苏打盐碱土改良研究[J].土壤通报,2001,32(增刊1):91-96.
谢正苗,吴卫红,徐建民.环境中氟化物的迁移和转化及其生态效应[J].环境科学进展,1999,7(2):41-54.
Anderon M A, Zehxy L W, Bertsch P M. Fhno-lunnmum complexes onmodel an sail exchanges[J].Soil Science Society of America Journal,1991,55:71-75.
Becker D E, Griffith J M, Hobbs C S, et al. The alleviation of fhronne toxicosis by means of ce itain abrmiuium com1-pounrds[J].Jounal of Anima1Science,1950,9:e647.
Maclean D C, Hansen K S, Selmeider R E. Amelioration of alurninunum toxicity in wheat by fluoride[J]New Phytologist,1992,121(l):81-88.
崔俊学.广东某地潮土和水稻土中氟形态转化及吸附研究[D].成都:成都理工大学,2010.
Hussain N, Ali A, Sarwar G, et al. Mechanism of salt tolerance in rice[J].Pedosphere,2003,13(3):233-238.
李洋洋.铝—氟互作对水稻及土壤中氟含量的影响研究[D].长春:吉林农业大学,2011.
生态环境部.GB 5084—2021农田灌溉水质标准[S].北京:生态环境部环境标准研究所,2021.
刘璇.吉林省西部高氟湖库底泥氟迁移转化的实验研究[D].长春:吉林大学,2011.
赵玲,金彬,马永军,等.水稻对氟化物吸收分布积累规律的分析[J].农业环境科学学报,2005(增刊1):52-55.
李日邦,郑达贤,王丽珍,等.土壤—植物生态系统中植物吸收氟的研究[J].地理学报,1986,41(2):123-131.
苑佰飞,马玉涛,包岩,等.水稻种植对吉林省西部苏打盐碱土改良培肥效果[J].水土保持学报,2019,33(3):320-326.
0
浏览量
904
下载量
0
CSCD
关联资源
相关文章
相关作者
相关机构
京公网安备11010802024621