当前位置:主页 > 硕博论文 > 工程硕士论文 >

镉污染条件下农田土壤微生物活性研究

发布时间:2019-03-12 21:25
【摘要】:重金属易通过大气沉降、肥料施用等途径进入农田土壤系统,长期以往会对土壤结构、微生物、动植物等造成严重的损害。农田环境质量的恶化,会导致农田丧失基本的生产能力。由于农田作物对镉具有较强的蓄积能力,镉通过一定的途径会对人体健康产生危害,因此,农田镉污染受到高度关注。农田土壤中微生物活性一定程度上能表征土壤中镉污染的程度,而国内外学者有通过测定土壤中酶活性来表征土壤中微生物活性,从而预测和评价镉污染的程度。但是不同地区的土壤理化性质的差异会导致酶活性的不同,从而影响农田镉污染程度的判断。本文选择苏州地区的水稻土、山林土和菜园土三种典型农田土壤作为研究对象,测定了水稻土、山林土和菜园土的基本理化性质,分别比较了三种不同农田土壤中过氧化氢酶、脲酶和蔗糖酶的活性。通过外源添加镉对三种农田土壤中过氧化氢酶、蔗糖酶和脲酶活性的影响以及土壤中不同形态镉的分布及变化,进一步探讨镉形态与酶活性之间的关系。最后研究了pH、有机质和盐分的变化对水稻土、菜园土和山林土中过氧化氢酶、脲酶和蔗糖酶活性的影响。主要得到以下结论:(1)由于土地利用方式的不同,在一定程度上会导致土壤理化性质的差异,通过水稻土、山林土和菜园土中酶活性的测定发现,过氧化氢酶活性表现为水稻土菜园土山林土,脲酶活性表现为水稻土菜园土山林土,蔗糖酶活性表现为水稻土山林土菜园土。(2)外源镉对水稻土、山林土和菜园土中过氧化氢酶、蔗糖酶和脲酶活性有抑制作用。随着外源镉浓度的升高,以及培养时间的增加,过氧化氢酶、蔗糖酶和脲酶活性均具有下降趋势。镉对脲酶和蔗糖酶的抑制作用,在山林土中强于水稻土和菜园土;对过氧化氢酶活性的抑制作用则是在水稻土中强于菜园土和山林土。(3)外源镉浓度较低时,初始水稻土中镉主要以可氧化态存在,潜在生物可利用态含量高;初始山林土和菜园土中镉主要以弱酸提取态存在,生物易利用态含量高。随着外源镉浓度的升高,水稻土、山林土和菜园土中镉的弱酸提取态含量增加,生物易利用态含量增加。而随着培养时间的增加,水稻土、山林土和菜园土中镉主要以弱酸提取态存在,但是弱酸提取态含量下降,生物易利用态含量下降,潜在生物可利用态含量增加,生物难利用态含量增加。(4)山林土、菜园土和水稻土中镉形态的分布和变化规律与酶活性呈现一定的相关性。随着镉浓度的升高,土壤中镉的生物易利用态含量增加,土壤中酶活性下降;随培养时间的增加,土壤中镉的生物易利用态含量减少,潜在生物可利用态含量增加,生物难利用态含量增加,酶活性呈下降趋势,但下降趋势幅度减弱。(5)pH、有机质和盐分变化对酶活性均有影响。随土壤pH值的升高,水稻土、山林土和菜园土中过氧化氢酶和脲酶活性呈现上升趋势,蔗糖酶的活性趋势表现为先上升后下降,说明土壤酸浓度的升高能够抑制过氧化氢酶、脲酶和蔗糖酶活性,过氧化氢酶和脲酶活性的升高是由于土壤中碱浓度升高所致,但会抑制蔗糖酶活性;随有机质含量的增加,水稻土、山林土和菜园土中过氧化氢酶和脲酶活性呈现上升趋势,说明土壤中有机质的增加能刺激土壤中酶活性的增加,在葡萄糖添加量为1%时,对土壤中脲酶有强刺激作用;随盐分含量的增加,水稻土、山林土和菜园土中过氧化氢酶活性下降,脲酶活性下降,蔗糖酶活性也下降,说明盐会抑制土壤中酶的正常功能与代谢。
[Abstract]:The heavy metal is easy to enter the farmland soil system through the way of atmospheric sedimentation, fertilizer application and the like, and can cause serious damage to the soil structure, the microorganism, the plant and the plant and the like for a long time. The deterioration of the environmental quality of the farmland can lead to the loss of basic production capacity of the farmland. As a result of the strong accumulation capacity of the farmland crops to the human body, the health of the human body can be caused by a certain way, and therefore, the pollution of the farmland is highly concerned. In that field, the activity of the microorganism in the soil can represent the degree of soil pollution in the soil to a certain extent, and the domestic and foreign scholars have the effect of determining the activity of the microorganism in the soil by measuring the activity of the enzyme in the soil, so as to predict and evaluate the degree of the soil pollution. However, the difference of the physical and chemical properties of the soil in different areas can lead to the difference of the enzyme activity, thus affecting the judgment of the pollution degree of the farmland. In this paper, three typical farmland soils of paddy soil, mountain forest and garden soil in Suzhou area are selected as the research object. The basic physical and chemical properties of paddy soil, mountain forest soil and vegetable garden soil are determined, and the activities of catalase, yeast enzyme and sucrase in the soil of three different fields are compared. The relationship between the enzyme activity and the activity of the catalase, the sucrase and the enzyme in the soil of the three agricultural fields and the distribution and the change of the different morphological characteristics of the soil were further discussed. The effects of changes of pH, organic matter and salt on the activity of catalase, catalase and sucrase in paddy soil, vegetable garden soil and mountain forest were studied. The results are as follows: (1) Because of the different land-use methods, the physical and chemical properties of the soil can be different to some extent, and the activity of the catalase in the soil of the paddy soil, the soil of the mountain and the soil of the garden soil has been found, and the activity of the catalase is shown as the soil of the soil and the soil of the paddy soil, The activity of the enzyme is as the soil of the soil and the soil of the soil of the paddy soil, and the activity of the sucrase is the soil of the soil and vegetable garden of the paddy soil. (2) The effect of exogenous yeast on the activity of catalase, sucrase and enzyme in paddy soil, forest soil and vegetable garden soil was inhibited. With the increase of the concentration of the exogenous enzyme and the increase of the culture time, the activity of the catalase, the sucrase and the enzyme of the enzyme has a downward trend. The inhibitory effect of the enzyme on the activity of the catalase and the sucrase is stronger than that of the paddy soil and the vegetable garden soil in the mountain forest soil, and the inhibition effect on the activity of the catalase is stronger than the garden soil and the mountain forest soil in the paddy soil. (3) When the concentration of the exogenous yeast is low, the initial paddy soil is mainly in the oxidizable state, and the potential bioavailable state content is high; the initial mountain forest soil and the vegetable garden soil are mainly in the weak acid extraction state, and the bioavailability is high. With the increase of the concentration of the exogenous yeast, the content of weak acid in paddy soil, the soil of the mountain and the soil of the vegetable garden is increased, and the content of the bioavailability is increased. However, with the increase of the culture time, the rice soil, the mountain forest soil and the vegetable garden soil are mainly in the weak acid extraction state, but the content of the weak acid extraction state is reduced, the bio-availability state content is reduced, the potential bioavailable state content is increased, and the biorefractory utilization state content is increased. (4) The distribution and the change of the morphology of the soil in the soil, the vegetable garden soil and the paddy soil have a certain correlation with the activity of the enzyme. As the concentration of the soil is increased, the biomass of the soil in the soil is increased, the activity of the enzyme in the soil is reduced, the biomass of the soil in the soil can be reduced with the increase of the culture time, the potential bioavailable state content is increased, and the biorefractory utilization state content is increased, The activity of the enzyme decreased, but the decrease of the decreasing trend. (5) The change of pH, organic matter and salt has an effect on the activity of the enzyme. As the pH value of the soil increases, the activity of the catalase and the enzyme in the paddy soil, the mountain forest soil and the vegetable garden soil shows a rising trend, the activity trend of the sucrose enzyme shows that the increase of the activity trend of the sucrose enzyme is first increased, and the increase of the concentration of the soil acid can inhibit the activity of the catalase, the yeast enzyme and the sucrase, the increase of the activity of the catalase and the enzyme is due to the increase of the concentration of the alkali in the soil, but the activity of the sucrase is inhibited; the activity of the catalase and the enzyme in the paddy soil, the mountain forest soil and the vegetable garden soil is increased with the increase of the content of the organic matter, the increase of the organic matter in the soil can stimulate the increase of the enzyme activity in the soil, and when the addition amount of the glucose is 1%, the enzyme in the soil has strong stimulation effect; the activity of the catalase in the paddy soil, the mountain forest soil and the garden soil is reduced with the increase of the salt content, and the enzyme activity is reduced, Sucrose enzyme activity also decreased, indicating that the salt would inhibit the normal function and metabolism of the enzyme in the soil.
【学位授予单位】:苏州科技大学
【学位级别】:硕士
【学位授予年份】:2017
【分类号】:X53

【相似文献】

相关期刊论文 前10条

1 ;什么是镉污染?[J];江苏氯碱;2010年01期

2 《中国经济周刊》评论员;;广西镉污染的冷思考[J];中国经济周刊;2012年05期

3 ;镉污染[J];吉林环境;2012年01期

4 冯克亮;日本某镉污染地区居民死亡率调查[J];环境与健康杂志;1988年04期

5 梁兰珍;日本石川县梯川流域镉污染区居民肾障碍的流行病学研究[J];环境与健康杂志;1990年06期

6 计时华;;镉污染区居民早期慢性镉中毒的诊断[J];环境保护科学;1992年03期

7 蔡诗文,,岳麟,袁一傲,徐兆发,孔庆瑚,尚琪;环境镉污染所致健康危害判定标准的研究[J];环境与健康杂志;1994年03期

8 汪再娟,金锋,唐红芳,周泽泽,王百辉;镉污染区居民的体镉负荷与硒元素水平相关性研究[J];广东微量元素科学;1999年06期

9 付宝荣,1李法云,1臧树良,1宋丽;锌营养条件下镉污染对小麦生理特性的影响[J];辽宁大学学报(自然科学版);2000年04期

10 刘占旗,罗福堂,高增林,常学章,庄晓玲;某铅锌矿及周围镉污染区镉接触者健康状况调查[J];中国公共卫生;2001年10期

相关会议论文 前10条

1 谢满廷;;环境镉污染对健康的影响[A];新观点新学说学术沙龙文集9:环境污染与人体健康[C];2007年

2 ;清除镉污染的研究[A];河北省土壤污染防治技术研讨会论文集[C];2010年

3 ;镉污染概述[A];河北省土壤污染防治技术研讨会论文集[C];2010年

4 徐兆发;裴秀丛;杨敬华;李北利;李革新;陈爱莉;蔺心芳;;张士镉污染区对成年妇女肾功能影响的追踪观察[A];全面建设小康社会:中国科技工作者的历史责任——中国科协2003年学术年会论文集(下)[C];2003年

5 钟祖标;;龙江河水镉污染之铁路应急处置工作分析[A];2012年铁路卫生防疫学术年会论文集[C];2012年

6 钱骁;刘瑞志;李捷;雷坤;富国;朱丽娜;;水体镉污染成因、应急处置及潜在风险评估[A];2012中国环境科学学会学术年会论文集(第四卷)[C];2012年

7 丁鸿;杨杏芬;王立斌;梁春穗;戴昌芳;黄善盛;陈子慧;杨颖;;广东省某市城区居民环境镉污染的暴露评估[A];第四届第二次中国毒理学会食品毒理学专业委员会与营养食品所毒理室联合召开学术会议论文集[C];2008年

8 冯思思;朱苗力;;试用苯并咪唑类化合物消除镉污染[A];第三届全国环境化学学术大会论文集[C];2005年

9 杨华;曹磊;刘钢;李青青;;潮褐土镉污染的有机调控机制及其修复途径研究[A];河北省土壤污染防治技术研讨会论文集[C];2010年

10 李顺江;赵同科;马茂亭;肖长坤;;不同施肥方式对土壤铬、镉污染及蔬菜中含量的影响[A];2013中国环境科学学会学术年会论文集(第五卷)[C];2013年

相关重要报纸文章 前10条

1 张绪才;“镉污染土地”产不出“无镉米”[N];中国质量报;2013年

2 记者 张莺 王存福 李斌;“奇迹说”背后的镉污染真相[N];新华每日电讯;2013年

3 “新华视点”记者 张莺 李斌;广西龙江镉污染“元凶”再次肇事[N];新华每日电讯;2014年

4 孟姝轶 记者 衣春翔;攻克治理镉污染世界难题[N];黑龙江日报;2014年

5 刘占旗;环境镉污染:不容忽视的健康威胁[N];中国环境报;2003年

6 罗中云;中国镉污染灾害初露苗头[N];北京科技报;2008年

7 欣宗;浏阳镉污染事件责任人受处罚[N];中国化工报;2009年

8 实习记者 彭立国 本报记者 夏晓柏;浏阳镉污染病理追踪:暴利之诱与监管之缺[N];21世纪经济报道;2009年

9 本报记者 陈永杰 叶子(实习);镉污染:监管不力的隐忧[N];北京科技报;2009年

10 本报记者 龙军;浏阳镉污染悲剧是如何酿成的[N];光明日报;2009年

相关博士学位论文 前1条

1 申屠佳丽;蔬菜系统镉污染的土壤化学与生物学响应及蔬菜安全诊断[D];浙江大学;2008年

相关硕士学位论文 前10条

1 张洁莹;广东省某地区镉污染损害人体健康调查研究[D];北京交通大学;2016年

2 沈秋悦;镉污染条件下农田土壤微生物活性研究[D];苏州科技大学;2017年

3 吴思英;镉污染对居民健康状况的影响[D];福建医科大学;2003年

4 朱飞;龙江水环境镉污染调查及对鱼类等水生生物的影响研究[D];广东工业大学;2013年

5 廖朱玮;镉污染黏土水泥固封机理及变形规律[D];武汉轻工大学;2014年

6 金铭;水稻镉污染胁迫高光谱分析模型研究[D];中国地质大学(北京);2011年

7 郭慧芬;环境汞、铅、镉污染对居民健康的影响[D];山西医科大学;2007年

8 韩天旭;环境铅、镉污染健康风险评价指标体系的构建及实证研究[D];华中科技大学;2012年

9 周少磊;非镉污染区人群尿镉、尿NAG及尿β_2-M等各指标含量的探讨[D];中国疾病预防控制中心;2012年

10 孙亮;环境镉接触人群铁状态与镉损伤的关系[D];遵义医学院;2012年



本文编号:2439170

资料下载
论文发表

本文链接:https://www.wllwen.com/shoufeilunwen/boshibiyelunwen/2439170.html


Copyright(c)文论论文网All Rights Reserved | 网站地图 |

版权申明:资料由用户34d7b***提供,本站仅收录摘要或目录,作者需要删除请E-mail邮箱bigeng88@qq.com