莫索灣灌區(qū)棉田土壤重金屬分布特征和評(píng)價(jià)及Cr污染修復(fù)效果研究
[Abstract]:In this paper, the distribution characteristics and accumulation of heavy metals in soils under cotton cultivation in Mosuowan Irrigation Area of Manas River Basin in Xinjiang were analyzed by means of regional investigation and field location test. The table of the study area was estimated by geostatistical interpolation method. The spatial distribution of heavy metals in soil layers provides basic data for the protection of soil environmental quality in cotton field of the irrigation area. The Cr element which is heavily polluted in the irrigation area is selected as the improvement object. Through indoor culture experiment, the effects of several chemical amendments on the distribution and transformation of Cr in soil are revealed. The main conclusions are as follows: (1) Cotton field The contents of heavy metals Cr, Ni, Cu, As and Pb in soils (0-100 cm) were 90.65, 32.22, 52.64, 10.90, 13.86 mg/kg, respectively, and those in wasteland soils were 78.21, 32.34, 44.16, 9.48, 13.91 mg/kg, respectively. The contents of Cr, Ni, Cu and As in cotton soils were significantly higher than those in wasteland, and higher than those in Xinjiang soils. The differences of Pb contents between the two soils were not significant, but lower than those in cotton soils. The variation coefficients of heavy metals in cotton soils were higher than those in wasteland soils, which belonged to moderate variation. The results showed that the accumulation of Cr, Cu, As and Ni in cotton field soil was mainly caused by the application of phosphorus fertilizer, but the correlation between heavy metal elements and N, P, K, pH in wasteland soil was not significant, which further explained the continuous cropping of cotton field. (3) The practicability of portable X-ray fluorescence spectrometer was studied and validated. The validation models R2 were 0.9124, 0.8979, 0.7723, 0.8729 mg/kg, respectively. The slope and intercept were optimized, which were close to the ideal model. The calibration results were compared with the traditional laboratory. The results of ICP-AES test showed a very significant positive correlation. The practicability of PXRF heterotopic method and the high accuracy of calibration curve can be fully proved by the validation model of secondary sampling of 36-50 soil samples. (4) Using portable X-ray fluorescence spectrometer to determine the heavy metal content in surface soil of irrigation area, the heavy metal content in soil can be determined quickly. Content variation function and model fitting showed that Cr, As were the best in exponential model, Ni, Pb were the best in Gaussian model, Cu was the best in spherical model, Cr and Cu were 0.86, 0.92 respectively, and the spatial autocorrelation was weak, which was influenced by human random factors. The spatial correlation of Ni, As and Pb were 0.57, 0.41 and 0.46, respectively, with moderate spatial correlation, which was followed by human activities. The results showed that Cr and As were slightly polluted and Ni were slightly polluted. (5) Pot experiment was used to study the remediation effect of different amendments on heavy metal Cr in soil. Exchangeable state content and soil pH value increase to a certain extent. With the increase of pollution concentration, the influence on pH value decreases gradually, but the effect of calcium magnesium phosphate fertilizer is better than CK.4. Exchangeable state content of soil first decreases and then increases, residual state content first increases and then decreases, and finally shows exchangeable state. The effect of the two modifiers was significantly higher than that of the activated carbon and straw, but their effect on the reduction of the exchangeable state content of Cr was shorter. The exchangeable state content of Cr increased after 42 days. The effect of straw application on soil pH and Cr exchangeable state content was not significant, which was related to the amount of improved application and cultivation time. The soil environment of cotton field in the whole irrigation area is not polluted, but it is close to the level of slight pollution. It is necessary to do a good job in the prevention and control of heavy metal pollution in the future planting process. Exchangeable state content decreased with time, which reduced the bioavailability of Cr in soil and achieved the purpose of remediation of Cr contaminated soil.
【學(xué)位授予單位】:石河子大學(xué)
【學(xué)位級(jí)別】:碩士
【學(xué)位授予年份】:2017
【分類號(hào)】:X53;X825
【參考文獻(xiàn)】
相關(guān)期刊論文 前10條
1 Somsubhra CHAKRABORTY;David C.WEINDORF;GARY J.MICHAELSON;Chien Lu PING;Ashok CHOUDHURY;Tarek KANDAKJI;Autumn ACREE;Akriti SHARMA;WANG Dandan;;In-Situ Differentiation of Acidic and Non-Acidic Tundra via Portable X-ray Fluorescence(PXRF) Spectrometry[J];Pedosphere;2016年04期
2 ZHENG Rong;ZHAO Jiale;ZHOU Xiu;MA Chao;WANG Li;GAO Xiaojiang;;Land Use Effects on the Distribution and Speciation of Heavy Metals and Arsenic in Coastal Soils on Chongming Island in the Yangtze River Estuary, China[J];Pedosphere;2016年01期
3 周長(zhǎng)松;鄒勝章;李錄娟;申豪勇;;幾種土壤重金屬污染評(píng)價(jià)方法的對(duì)比[J];地球與環(huán)境;2015年06期
4 高鵬;劉勇;蘇超;;太原城區(qū)周邊土壤重金屬分布特征及生態(tài)風(fēng)險(xiǎn)評(píng)價(jià)[J];農(nóng)業(yè)環(huán)境科學(xué)學(xué)報(bào);2015年05期
5 張?zhí)祢?劉剛;王圣偉;;基于GIS/RS的不同土地利用類型重金屬面源污染比較[J];農(nóng)業(yè)機(jī)械學(xué)報(bào);2014年S1期
6 劉延;常薇;何小茹;;分光光度法測(cè)定紡織品中可萃取重金屬銅[J];應(yīng)用化工;2013年12期
7 樊霆;葉文玲;陳海燕;魯洪娟;張穎慧;李定心;唐子陽(yáng);馬友華;;農(nóng)田土壤重金屬污染狀況及修復(fù)技術(shù)研究[J];生態(tài)環(huán)境學(xué)報(bào);2013年10期
8 侯冠宇;王平;佟存柱;;激光誘導(dǎo)擊穿光譜技術(shù)及應(yīng)用研究進(jìn)展[J];中國(guó)光學(xué);2013年04期
9 穆葉賽爾·吐地;吉力力·阿布都外力;姜逢清;;天山北坡土壤重金屬含量的分布特征及其來(lái)源解釋[J];中國(guó)生態(tài)農(nóng)業(yè)學(xué)報(bào);2013年07期
10 馬子龍;毛瀟萱;丁中原;高宏;黃韜;田慧;郭強(qiáng);;新疆哈密地區(qū)有機(jī)氯農(nóng)藥大氣、土壤殘留特征、氣-土交換及潛在生態(tài)風(fēng)險(xiǎn)[J];環(huán)境科學(xué);2013年03期
相關(guān)博士學(xué)位論文 前2條
1 韓春麗;新疆棉花長(zhǎng)期連作土壤養(yǎng)分時(shí)空變化及可持續(xù)利用研究[D];石河子大學(xué);2010年
2 楊秀敏;重金屬?gòu)?fù)合污染土壤的粘土礦物與生物綜合修復(fù)技術(shù)研究[D];中國(guó)礦業(yè)大學(xué)(北京);2009年
相關(guān)碩士學(xué)位論文 前5條
1 李鵬;農(nóng)田土壤重金屬Cd、Cu、和As污染評(píng)價(jià)及修復(fù)技術(shù)研究[D];武漢理工大學(xué);2011年
2 陳志明;不同改良劑修復(fù)重金屬鉻污染土壤的研究[D];山東農(nóng)業(yè)大學(xué);2010年
3 李夏;有機(jī)無(wú)機(jī)改良劑對(duì)鉛污染紅壤中鉛形態(tài)及其植物有效性的影響[D];浙江大學(xué);2010年
4 孫淑芹;福州市典型工業(yè)區(qū)土壤污染特征分析及其評(píng)價(jià)研究[D];福建農(nóng)林大學(xué);2009年
5 周華;不同改良劑對(duì)Cd、Pb污染土壤改良效果的研究[D];華中農(nóng)業(yè)大學(xué);2003年
,本文編號(hào):2225383
本文鏈接:http://sikaile.net/shengtaihuanjingbaohulunwen/2225383.html