生物炭基针铁矿复合材料对水中莠去津吸附特性研究

doi:10.16258/j.cnki.1674-5906.2021.10.013

生态环境学报 ›› 2021, Vol. 30 ›› Issue (10): 2067-2075.DOI: 10.16258/j.cnki.1674-5906.2021.10.013

生物炭基针铁矿复合材料对水中莠去津吸附特性研究

丛鑫(), 李瑶, 王宇, 郑力

辽宁工程技术大学环境科学与工程学院,辽宁阜新 123000

收稿日期:2021-09-18 出版日期:2021-10-18 发布日期:2021-12-21
作者简介:丛鑫（1976年生）,女,教授,博士,研究方向为土壤环境化学和生态修复。E-mail: congxin1800@163.com
基金资助:
国家重点研发计划项目(2019YFC1803800);辽宁工程技术大学学科创新团队资助项目(LNTU20TD-24)

Adsorption Characterization of Atrazine in Aqueous Medium on Goethite Biochar Composites

CONG Xin(), LI Yao, WANG Yu, ZHENG Li

College of Environmental Science and Engineering, Liaoning Engineering Technology University, Fuxin 123000, China

Received:2021-09-18 Online:2021-10-18 Published:2021-12-21

摘要/Abstract

摘要：

以牛粪和水稻秸秆为原料,分别在300 ℃和500 ℃条件下制备生物炭,同时通过共沉淀方法制备生物炭基针铁矿复合材料,研究生物炭及生物炭基复合材料对水中莠去津吸附特征。SEM和XRD分析结果表明,复合材料表面粗糙程度增加,2θ在21.2°、33.4°、36.6°、47.6°处出现针铁矿的特征衍射峰,生物炭基针铁矿复合材料制备成功。通过对吸附动力学和等温吸附平衡分析发现,生物炭对莠去津的吸附行为更符合准二级动力学方程,等温吸附过程符合Freundlich模型（r²为0.925—0.996）。在25 ℃条件下,莠去津在300 ℃和500 ℃条件下制备的针铁矿负载牛粪生物炭上的吸附量分别是原生物炭上吸附量的1.59倍和2.99倍,在针铁矿负载水稻秸秆生物炭上的吸附量分别是原生物炭上吸附量的2.02倍和1.73倍。比表面积和孔结构数据显示,生物炭基复合材料的比表面积是原生物炭材料的4.41—20.8倍,制备生物炭材料的孔结构以中孔为主。莠去津在生物炭上的吸附大体表现为吸热的自发过程。对不同材料制备的生物炭及与生物炭基复合材料吸附性能进行对比,结果表明水稻秸秆制备的生物炭对莠去津的吸附性能优于牛粪制备的生物炭,生物炭基针铁矿复合材料对莠去津的吸附效果优于原生物炭。随制备温度的升高,相同材料生物炭对莠去津吸附性能略有增加。研究结果可为生物炭及生物炭基针铁矿复合材料去除水中莠去津的应用提供理论依据。

关键词: 生物炭基针铁矿, 莠去津, 吸附性能, 牛粪生物炭, 水稻秸秆生物炭

Abstract:

Cow dung and rice straw were chosen as raw materials to prepare biochar at 300 ℃ and 500 ℃, respectively. Meanwhile, goethite biochar composites were prepared through co-precipitation of the iron metal ions onto biochar to study the adsorption characterization of atrazine in aqueous medium on biochars and goethite biochar composites. The results of scanning electron microscopy (SEM) and X-ray diffraction (XRD) analysis showed that the surface roughness of the composites increased, and the peaks at 2θ=21.2°, 33.4°, 36.6° and 47.6° could be agreed well with the standard othorhombic phase of goethite, which suggested goethite biochar composites were successfully prepared. The study of adsorption kinetics and isotherms showed that the adsorption process of atrazine on biochars was in accordance with quasi-second-order kinetic equations, and the isothermal adsorption process was well fitted to Freundlich model (r²: 0.92-0.996). At 25 ℃, The adsorption capacities of atrazine on the goethite-loaded cow dung biochar prepared at 300 and 500 ℃ was 1.59 and 2.99 times, and the adsorption capacities on the goethite-loaded rice straw biochar was 2.02 and 1.73 times than those of the original biochar, respectively. The analysis of specific surface area and pore structure showed that the specific surface areas of biochar composites were 4.41-20.8 times than those of the original biochar materials. Mesoporous was the main pore structure of the prepared biochar materials. Thermodynamic analysis showed that the adsorption process of atrazine on biochar was spontaneous and endothermic. The biochar prepared from rice straw had better adsorption capacity for atrazine than that prepared from cow dung. The adsorption properties of atrazine on biochars showed that goethite biochar composites had better adsorption capacity for atrazine than the original biochar did. With the increase of preparation temperature, the adsorption capacities of atrazine on biochars increased slightly. The results have certain theoretical significance for the application of biochars and goethite biochar composites in the treatment of wastewater containing atrazine residues.

Key words: goethite biochar composites, atrazine, adsorption characteristics, cow dung biochar, rice straw biochar

中图分类号:

丛鑫, 李瑶, 王宇, 郑力. 生物炭基针铁矿复合材料对水中莠去津吸附特性研究[J]. 生态环境学报, 2021, 30(10): 2067-2075.

CONG Xin, LI Yao, WANG Yu, ZHENG Li. Adsorption Characterization of Atrazine in Aqueous Medium on Goethite Biochar Composites[J]. Ecology and Environment, 2021, 30(10): 2067-2075.

图/表 8

图1 生物炭及生物炭基针铁矿复合材料XRD图谱 N300、N500分别为300、500 ℃下制备的牛粪生物炭;J300和J500分别为300、500 ℃条件下制备的水稻秸秆生物炭。下同

Fig. 1 XRD spectra of biochar and goethite biochar composites

图2 生物炭及生物炭基针铁矿复合材料SEM图

Fig. 2 SEM images of biochar and biochar compsites

表1 生物炭及生物炭基针铁矿复合材料理化性质

Table 1 Physical and chemical properties of biochar and biochar goethite composites

生物炭种类 Types of biochar	元素原子百分比 Atomic percentage of element/%				比表面积 Specific surface area/ (m²∙g^-1)	孔结构分析 Pore structure analysis
生物炭种类 Types of biochar	C	O	Fe	S	比表面积 Specific surface area/ (m²∙g^-1)	最可几孔径 Mode pore size/nm	平均孔径 Mean pore size/nm	总孔体积 Total pore volume/(cm³∙g^-1)
N300	69.28	30.21	0.43	0.08	1.995	3.452	9.055	0.0079
N500	73.45	26.48	0.03	0.03	4.437	3.726	14.78	0.0785
J300	89.74	10.22	0.01	0.04	16.11	3.048	4.575	0.0412
J500	50.02	49.48	0.18	0.32	36.06	3.779	11.91	0.0435
GN300	66.28	30.65	2.84	0.22	35.43	3.396	15.83	0.1309
GN500	90.44	8.79	0.66	0.11	92.13	3.398	15.88	0.2086
GJ300	84.57	13.8	1.63	0	154.2	3.402	13.61	0.5416
GJ500	71.35	27.62	0.95	0.08	159.1	3.403	16.39	0.6321

图3 莠去津在生物炭及其复合材料上吸附动力学曲线

Fig. 3 Kinetics curves of atrazine adsorption on biochars and their composites

表2 莠去津在生物炭及其复合材料上吸附动力学参数

Table 2 Kinetic equation parameters of atrazine adsorption on biochars and their composites

生物炭类型 Types of biochar	准一级动力学方程 Pseudo first-order kinetic equation			准二级动力学方程 Pseudo second-order kinetic equation			双常数方程 Double-constant equation
生物炭类型 Types of biochar	q_e/(mg∙g^-1)	k₁/h^-1	r²	q_e/(mg∙g^-1)	k₂/(g∙mg^-1∙h^-1)	r²	lna	K_s/(mg∙g^-1∙h^-1)	r²
N300	0.612	0.157	0.962	0.694	0.703	0.990	-1.445	0.313	0.989
N500	0.452	0.211	0.898	0.528	0.513	0.995	-1.347	0.201	0.972
J300	4.973	0.659	0.883	5.573	0.222	0.998	1.126	0.178	0.966
J500	4.454	0.232	0.823	5.125	0.202	0.996	1.067	0.163	0.986
GN300	1.323	0.158	0.978	1.468	0.331	0.992	-0.775	0.344	0.975
GN500	1.529	0.186	0.990	1.677	0.318	0.994	-0.612	0.339	0.968
GJ300	10.82	0.474	0.866	12.21	0.122	0.998	2.095	0.116	0.992
GJ500	8.097	0.237	0.729	9.274	0.112	0.997	1.617	0.178	0.967

图4 莠去津在生物炭及其复合材料上吸附等温线

Fig. 4 Adsorption isotherms of atrazine on biochars and their composites

表3 莠去津在生物炭及其复合材料上等温吸附模型参数

Table 3 The parameters of isothermal adsorption model of atrazine on biochars and their composites

生物炭类型 Types of biochars	温度 Temperature/K	Freundlich Model		$\lg q_{e} = \lg k_{f} + \frac{1}{n} \lg ρ_{e}$		Langmuir Model	$\frac{1}{q_{e}} = \frac{1}{Q_{max}} + \frac{1}{Q_{max} b} \cdot \frac{1}{ρ_{e}}$
生物炭类型 Types of biochars	温度 Temperature/K	n	K_F	r²	K_oc/(L·g^-1）	Q_max/(mg·L^-1）	b	r²
N300	298.15	0.869	0.091	0.991	0.498	8.355	0.009	0.992
	308.15	0.858	0.107	0.995	0.687	8.853	0.009	0.991
	318.15	0.853	0.143	0.995	0.920	10.96	0.010	0.991
N500	298.15	0.650	0.089	0.995	0.673	1.324	0.046	0.988
	308.15	0.584	0.132	0.987	1.033	1.362	0.065	0.977
	318.15	0.544	0.193	0.982	1.492	1.584	0.084	0.973
J300	298.15	0.393	2.090	0.958	12.17	7.823	0.266	0.951
	308.15	0.356	2.677	0.987	15.06	8.379	0.385	0.888
	318.15	0.348	3.505	0.937	19.29	10.11	0.462	0.923
J500	298.15	0.327	2.190	0.925	23.22	6.197	0.462	0.939
	308.15	0.364	2.726	0.940	27.85	8.785	0.363	0.881
	318.15	0.297	3.821	0.937	37.29	9.351	0.682	0.880
GN300	298.15	0.677	0.208	0.995	1.448	3.363	0.045	0.998
	308.15	0.716	0.126	0.996	0.852	2.924	0.030	0.990
	318.15	0.651	0.119	0.992	0.890	1.732	0.048	0.981
GN500	298.15	0.705	0.229	0.989	1.449	4.397	0.038	0.993
	308.15	0.691	0.249	0.993	1.588	4.576	0.038	0.997
	318.15	0.696	0.262	0.992	1.846	5.252	0.034	0.981
GJ300	298.15	0.371	4.378	0.991	21.48	15.42	0.253	0.959
	308.15	0.429	3.228	0.993	17.60	14.20	0.200	0.980
	318.15	0.483	2.278	0.985	12.76	13.04	0.134	0.968
GJ500	298.15	0.413	2.918	0.976	29.57	11.80	0.234	0.984
	308.15	0.414	3.095	0.980	31.00	12.52	0.232	0.954
	318.15	0.374	3.716	0.994	36.04	13.19	0.254	0.924

表3 莠去津在生物炭及其复合材料上等温吸附模型参数

Table 3 The parameters of isothermal adsorption model of atrazine on biochars and their composites

生物炭类型 Types of biochars	温度 Temperature/K	Freundlich Model		$\lg q_{e} = \lg k_{f} + \frac{1}{n} \lg ρ_{e}$		Langmuir Model	$\frac{1}{q_{e}} = \frac{1}{Q_{max}} + \frac{1}{Q_{max} b} \cdot \frac{1}{ρ_{e}}$
生物炭类型 Types of biochars	温度 Temperature/K	n	K_F	r²	K_oc/(L·g^-1）	Q_max/(mg·L^-1）	b	r²
N300	298.15	0.869	0.091	0.991	0.498	8.355	0.009	0.992
	308.15	0.858	0.107	0.995	0.687	8.853	0.009	0.991
	318.15	0.853	0.143	0.995	0.920	10.96	0.010	0.991
N500	298.15	0.650	0.089	0.995	0.673	1.324	0.046	0.988
	308.15	0.584	0.132	0.987	1.033	1.362	0.065	0.977
	318.15	0.544	0.193	0.982	1.492	1.584	0.084	0.973
J300	298.15	0.393	2.090	0.958	12.17	7.823	0.266	0.951
	308.15	0.356	2.677	0.987	15.06	8.379	0.385	0.888
	318.15	0.348	3.505	0.937	19.29	10.11	0.462	0.923
J500	298.15	0.327	2.190	0.925	23.22	6.197	0.462	0.939
	308.15	0.364	2.726	0.940	27.85	8.785	0.363	0.881
	318.15	0.297	3.821	0.937	37.29	9.351	0.682	0.880
GN300	298.15	0.677	0.208	0.995	1.448	3.363	0.045	0.998
	308.15	0.716	0.126	0.996	0.852	2.924	0.030	0.990
	318.15	0.651	0.119	0.992	0.890	1.732	0.048	0.981
GN500	298.15	0.705	0.229	0.989	1.449	4.397	0.038	0.993
	308.15	0.691	0.249	0.993	1.588	4.576	0.038	0.997
	318.15	0.696	0.262	0.992	1.846	5.252	0.034	0.981
GJ300	298.15	0.371	4.378	0.991	21.48	15.42	0.253	0.959
	308.15	0.429	3.228	0.993	17.60	14.20	0.200	0.980
	318.15	0.483	2.278	0.985	12.76	13.04	0.134	0.968
GJ500	298.15	0.413	2.918	0.976	29.57	11.80	0.234	0.984
	308.15	0.414	3.095	0.980	31.00	12.52	0.232	0.954
	318.15	0.374	3.716	0.994	36.04	13.19	0.254	0.924

表4 莠去津在生物炭及其复合材料上吸附热力学参数

Table 4 Thermodynamic parameters of atrazine adsorption on biochars and their composites

Types of biochars	Temperature/ K	ΔG⁰/ (kJ∙mol^-1)	ΔH⁰/ (kJ∙mol^-1)	ΔS⁰/ (kJ∙mol^-1∙K^-1)	Types of biochars	Temperature/ K	ΔG⁰/ (kJ∙mol^-1)	ΔH⁰/ (kJ∙mol^-1)	ΔS⁰/ (kJ∙mol^-1∙K^-1)
N300	298.15	-11.15	18.26	0.098	GN300	298.15	-13.23	-22.01	-0.03
	308.15	-11.97				308.15	-12.31
	318.15	-13.12				318.15	-12.65
N500	298.15	-11.13	30.58	0.140	GN500	298.15	-13.47	5.35	0.06
	308.15	-12.51				308.15	-14.07
	318.15	-13.92				318.15	-14.73
J300	298.15	-18.95	20.37	0.132	GJ300	298.15	-20.78	-25.73	-0.02
	308.15	-20.22				308.15	-20.70
	318.15	-21.59				318.15	-20.45
J500	298.15	-19.07	21.89	0.137	GJ500	298.15	-19.78	9.48	0.10
	308.15	-20.27				308.15	-20.59
	318.15	-21.82				318.15	-21.74

参考文献 36

[1]	CASTRO C S, GUERREIRO M C, GONCALVES M, et al., 2009. Activated carbon/iron oxide composites for the removal of atrazine from aqueous medium[J]. Journal of hazardous materials, 164(2-3):609-614. DOI URL
[2]	CHEN B L, CHEN Z M, LV S F, 2011. A novel magnetic biochar efficiently sorbs organic pollutants and phosphate[J]. Bioresource Technology, 102(2):716-723. DOI URL
[3]	GUO X T, DONG H, YANG C, et al., 2016. Application of goethite modified biochar for tylosin removal from aqueous solution[J]. Colloids and Surfaces A: Physicochemical and Engineering Aspects, 502:81-88. DOI URL
[4]	LI B, YANG L, WANG C Q, et al., 2017. Adsorption of Cd(II) from aqueous solutions by rape straw biochar derived from different modification processes[J]. Chemosphere, 175:332-340. DOI URL
[5]	LIU N, CHARRUA A B, WENG C H, et al., 2015. Characterization of biochars derived from agriculture wastes and their adsorptive removal of atrazine from aqueous solution: A comparative study[J]. Bioresource Technology, 198:55-62. DOI URL
[6]	QU M J, LI H D, LI N, et al., 2017. Distribution of atrazine and its phytoremediation by submerged macrophytes in lake sediments[J]. Chemosphere, 168:1515-1522. DOI URL
[7]	SUN K, GAO B, ZHANG Z Y, et al., 2010. Sorption of atrazine and phenanthrene by organic matter fractions in soil and sediment[J]. Envrionmental Pollution, 158(12):3520-3526.
[8]	TAO Y, HU S B, HAN S Y, et al., 2019. Efficient removal of atrazine by iron-modified biochar loaded Acinetobacter lwoffii DNS32[J]. Science of the Total Environment, 682:59-69. DOI URL
[9]	WANG H, CHU Y X, FANG C G, et al., 2017. Sorption of tetracycline on biochar derived from rice straw under different temperatures[J]. Plos One, 12(8):1-14.
[10]	WANG H, FANG C G, WANG Q, et al., 2018. Sorption of tetracycline on biochar derived from rice straw and swine manure[J]. RSC Advances, 8(29):16260-16268. DOI URL
[11]	YANG F, SUN L L, XIE W L, et al., 2017. Nitrogen-functionalization biochars derived from wheat straws via molten salt synjournal: An efficient adsorbent for atrazine removal[J]. Science of the Total Envrionment, 607-608:1391-1399.
[12]	ZHANG Z S, WANG X J, WANG Y, et al., 2013. Pb(Ⅱ) removal from water using Fe-coated bamboo charcoal with the assistance of microwaves[J]. Journal of Environmental Science, 25(5):1044-1053.
[13]	ZHU S H, ZHAO J J, ZHAO N, et al., 2020. Goethite modified biochar as a multifunctional amendment for cationic Cd(Ⅱ), anionic As(Ⅲ), roxarsone, and phosphorus in soil and water[J]. Journal of Cleaner Production, 247:1-10.
[14]	CHARRUA A B, 2015. 生物碳吸附去除溶液中的阿特拉津[D]. 吉林: 吉林大学.
	CHARRUA A B, 2015. Adsorptive removal of atrazine from aqueous solution by various types of biochars[D]. Jilin: Jilin University.
[15]	程婉艺, 2020. 改性生物炭有机复合材料的制备及吸附性能的研究[D]. 青岛: 青岛科技大学.
	CHENG W Y, 2020. Preparation and adsorption capability of modified biochar composites[D]. Qingdao: Qingdao University of Science and Technology.
[16]	程扬, 沈启斌, 刘子丹, 等, 2019. 两种生物炭的制备及其对水溶液中四环素去除的影响因素[J]. 环境科学, 40(3):1328-1336.
	CHENG Y, SHEN Q B, LIU Z D, et al., 2019. Preparation of two kinds of biochar and the factors influencing tetracycline removal from aqueous solution[J]. Environmental Science, 40(3):1328-1336.
[17]	邓雅雯, 晏彩霞, 聂明华, 等, 2020. 生物炭对抗生素的吸附/解吸研究进展[J]. 环境污染与防治, 42(3):376-384.
	DENG Y W, YAN C X, NIE M H, et al., 2020. Study on the antibiotic adsorption/desorption of biochar: A review[J]. Environmental Pollution and Control, 42(3):376-384.
[18]	樊玉娜, 2019. 高羊茅生物炭对不同类型土壤中阿特拉津及其代谢产物吸附能力的影响研究[D]. 曲阜: 曲阜师范大学.
	FAN Y N, 2019. Effects of tall festuca biochar on the adsorption capacity of Atrazine and its metabolites in different types of soils[D]. Qufu: Qufu Normal University.
[19]	冯婧微, 徐英侠, 兰希平, 2014. 改性纳米零价铁去除水中莠去津[J]. 农药, 53(9):651-654.
	FENG J W, XU Y X, LAN X P, 2014. Removal of atrazine in wastewater using modified nanoscale zero-valent iron[J]. Agrochemicals, 53(9):651-654.
[20]	李昉泽, 冯丹, 邓惠, 等, 2015. 阿特拉津在5种农业土壤中的吸附解吸特性分析[J]. 生态环境学报, 24(12):2056-2061.
	LI F Z, FENG D, DENG H, et al., 2015. Adsorption and desorption of atrazine in five agriculture soils[J]. Ecology and Environmental Sciences, 24(12):2056-2061.
[21]	廖家辉, 2014. AFT在“氧化铁-腐殖质-Pb²⁺”系统中的吸附及土壤中AFT/Pb²⁺检测的生物传感新方法[D]. 重庆: 西南大学.
	LIAO J H, 2014. Adsorption of AFT in “iron oxide-humus-Pb²⁺” system and new biosensing methods for AFT/Pb²⁺ measurement in soil[D]. Chongqing: Southwest University.
[22]	刘娜, 杨亚冬, ALBERTO B C, 等, 2016. 响应曲面法优化生物质炭去除水溶液中的阿特拉津[J]. 吉林大学学报(地球科学版), 46(4):1199-1207.
	LIU N, YANG Y D, ALBERTO B C, et al., 2016. Optimization of atrazine removal from aqueous solution by biochar using response surface methodology[J]. Journal of Jilin University (Earth Science Edition), 46(4):1199-1207.
[23]	阮梦娜, 王宇芳, 楼筱珺, 等, 2016. 生物炭耦合菌剂法去除污染水体中的苯胺[J]. 环境工程学报, 10(5):2454-2458.
	RUAN M N, WANG Y F, LOU X J, et al., 2016. Aniline removal with biochar coupling microbial agents[J]. Chinese Journal of Environmental Engineering, 10(5):2454-2458.
[24]	宋桃莉, 伊学农, 王玉琳, 等, 2013. 超声协同Feton法与类Feton法预处理莠去津农药废水研究[J]. 水资源与水工程学报, 24(6):153-156.
	SONG T L, YI X N, WANG Y L, et al., 2013. Study on pretreatment of atrazine pesticide wastewater by ultrasound coupling with Fenton and Fenton-like methods[J]. Journal of Water Resources and water Engineering, 24(6):153-156.
[25]	孙莉莉, 2019. 不同粒径生物炭对水溶液中阿特拉津和铅的吸附行为研究[D]. 哈尔滨: 东北农业大学.
	SUN L L, 2019. Adsorption of atrazine and lead in aqueous solution onto biochars of different particle sizes[D]. Harbin: Northeast Agricultural University.
[26]	王靖宜, 王丽, 张文龙, 等, 2019. 生物炭基复合材料制备及其对水体特征污染物的吸附性能[J]. 化工进展, 38(8):3838-3851.
	WANG J Y, WANG L, ZHANG W L, et al., 2019. Preparation of biochar-based composites and their adsorption performances for characteristic contaminants in wastewater[J]. Chemical Industry and Engineering Progress, 38(8):3838-3851.
[27]	王晟, 冯翔, 李兵, 等, 2021. 多种铁改性和未改性生物炭对模拟地下水中六价铬的去除[J]. 吉林大学学报(地球科学版), 51(1):247-255.
	WANG S, FENG X, LI B, et al., 2021. Removal of hexavalent chromium from simulated groundwater by variety of iron-modified and unmodified biochars[J]. Journal of Jilin University (Earth Science Edition), 51(1):247-255.
[28]	王旭峰, 郑立安, 刘毛, 等, 2017. 改性玉米芯生物炭对废水中铜和氨氮的吸附[J]. 工业水处理, 37(1):37-41.
	WANG X F, ZHENG L A, LIU M, et al., 2017. Adsorption characters of Cu²⁺ and NH₄⁺-N in wastewater by modified corncob biochar[J]. Industrial Water Treatment, 37(1):37-41.
[29]	魏茁, 姜英宇, 陈立飞, 等, 2021. Fe & Cu生物炭复合材料脱除污染水体中金霉素[J]. 生态环境学报, 30(4):805-815.
	WEI Z, JIANG Y Y, CHEN L F, et al., 2021. Fe & Cu-biochar composite material to remove chlortetracycline from polluted water[J]. Ecology and Environmental Sciences, 30(4):805-815.
[30]	徐雄, 李春梅, 孙静, 等, 2016. 我国重点流域地表水中29种农药污染及其生态风险评价[J]. 生态毒理学报, 11(2):347-354.
	XU X, LI C M, SUN J, et al., 2016. Residue characteristics and ecological risk assessment of twenty-nine pesticides in surface water of major river-basin in China[J]. Asian Journal of Ecotoxicology, 11(2):347-354.
[31]	徐雪斌, 丁竹红, 胡忻, 等, 2017. 花生壳基和木屑基生物炭对离子型染料Pb(Ⅱ)的吸附性能研究[J]. 环境污染与防治, 39(9):929-935.
	XU X B, DING Z H, HU X, et al., 2017. Study on the antibiotic adsorption/desorption of biochar: A review[J]. Environmentl Pollution and Control, 39(9):929-935.
[32]	俞花美, 2014. 生物质炭对环境中阿特拉津的吸附解吸作用及机理研究[D]. 北京: 中国矿业大学(北京).
	YU H M, 2014. Sorption/desorption characteristics and mechanisms of bio-chars with atrazine in environment[D]. Beijing: China University of Mining and Technology (Beijing).
[33]	张海波, 苏龙, 程红艳, 等, 2021. 不同热解温度制备的香菇菌糠生物炭对孔雀石绿的吸附及其机理分析[J]. 核农学报, 35(5):1231-1242.
	ZHANG H B, SU L, CHENG H Y, et al., 2021. Adsorption and mechanism analysis of Malachite green adsorption by spent Lentinus edodes substrate based biochar prepared at different pyrolysis temperatures[J]. Journal of nuclear agricultural science, 35(5):1231-1242.
[34]	张苏明, 张建强, 周凯, 等, 2021. 铁基改性椰壳生物炭对砷的吸附效果及机制研究[J]. 生态环境学报, 30(7):1503-1512.
	ZHANG S M, ZHANG J Q, ZHOU K, et al., 2021. Adsorption effect and mechanism of iron-based modified coconut shell biochar to arsenic[J]. Ecology and Environmental Sciences, 30(7):1503-1512.
[35]	张晓蕾, 薛文平, 徐恒振, 等, 2012. 近海沉积物对粪固醇的等温吸附和热力学研究[J]. 环境科学, 33(10):3547-3553.
	ZHANG X L, XUE W P, XU H Z, et al., 2012. Sorption isotherms and sorption thermodynamics of faecal sterols on offshore sediment[J]. Environmental Science, 33(10):3547-3553.
[36]	张照然, 2020. 生物炭基复合材料去除水中磷酸盐的应用研究[D]. 济南: 济南大学.
	ZHANG Z R, 2020. Applied study on the removal of phosphate from aqueous solutions by biochar based composites[D]. Ji’nan: University of Ji’nan.

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生物炭基针铁矿复合材料对水中莠去津吸附特性研究

Adsorption Characterization of Atrazine in Aqueous Medium on Goethite Biochar Composites

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