天堂国产午夜亚洲专区-少妇人妻综合久久蜜臀-国产成人户外露出视频在线-国产91传媒一区二区三区

當(dāng)前位置:主頁 > 科技論文 > 化工論文 >

電鍍場地土壤重金屬元素Cr、Zn、Cu形態(tài)分析及土壤修復(fù)

發(fā)布時間:2018-11-26 07:54
【摘要】:根據(jù)重金屬的毒性及污染嚴(yán)重程度,將重金屬防控對象分為2類,第一類重金屬防控對象是以鉛、汞、鎘、鉻和類金屬砷等污染嚴(yán)重的重金屬元素為主;第二類防控對象是鉈、錳、鎳、鋅、銅等,這也是環(huán)保部在《重金屬污染綜合防治"十二五"規(guī)劃》中明確規(guī)定的防控原則。目前國家環(huán)保管理部門對重金屬污染排放實(shí)行嚴(yán)格的總量控制制度,并把這些污染區(qū)域分為重點(diǎn)區(qū)域和非重點(diǎn)區(qū)域。重金屬土壤污染不僅影響著生態(tài)環(huán)境,而且對其他環(huán)境的安全也會造成嚴(yán)重的影響。在我國隨著城市人口的增加及規(guī)模的擴(kuò)建,新的城市區(qū)域規(guī)劃要求人口密集的城區(qū)內(nèi)的重污染企業(yè)要退城進(jìn)園,搬遷后的廠區(qū)必須進(jìn)行環(huán)境影響評估,對于已污染的廠區(qū)土壤必須進(jìn)行治理修復(fù)方可作為城市用地新用途的使用,因此退城進(jìn)園及企業(yè)搬遷后的污染場區(qū)土壤的修復(fù)工作就顯得尤為重要;土壤中的重金屬污染防治和土壤修復(fù)的工作已成為當(dāng)今環(huán)境保護(hù)工作者的重大研究內(nèi)容。本文以搬遷后的電鍍企業(yè)重金屬污染場地作為土壤修復(fù)的研究對象,為了規(guī)范發(fā)展電鍍行業(yè)排放的污染物對環(huán)境的污染,進(jìn)一步整合各種資源,發(fā)揮電鍍行業(yè)集中建設(shè),控制規(guī)模優(yōu)勢和輻射帶動效應(yīng),保障電鍍行業(yè)健康穩(wěn)定發(fā)展,山東省某高壓開關(guān)有限公司電鍍生產(chǎn)線需整體搬遷,根據(jù)當(dāng)?shù)爻鞘幸?guī)劃及環(huán)保要求,該企業(yè)現(xiàn)已遷往規(guī)劃后的化工工業(yè)園,原址場污染土壤需要進(jìn)行治理修復(fù),原廠址的污染土壤需要進(jìn)行修復(fù),修復(fù)面積約為7452m2。該企業(yè)搬遷前以生產(chǎn)各種類型的電器元件為產(chǎn)品,生產(chǎn)工藝需要大量的電鍍環(huán)節(jié),電鍍元件涉及到的重金屬為鉻、銅、鋅;搬遷后規(guī)劃的該場地用途為商業(yè)用地,污染場地修復(fù)目標(biāo)主要采用《土壤環(huán)境質(zhì)量標(biāo)準(zhǔn)》(GB15618—1995)三級標(biāo)準(zhǔn)值。通過對原廠區(qū)土壤取樣測定,測定結(jié)果顯示污染場地土壤樣品中六價鉻最大濃度達(dá)到41.7mg/kg,總鉻最大濃度達(dá)到4150mg/kg,Cu的最大濃度達(dá)2220mg/kg,Zn最大濃度達(dá)5020mg/kg,遠(yuǎn)超《土壤環(huán)境質(zhì)量標(biāo)準(zhǔn)》(GB15618—1995)三級標(biāo)準(zhǔn)限值。歐美日等發(fā)達(dá)國家已把固化穩(wěn)定化處置技術(shù)(S/S法)作為一種常用的修復(fù)技術(shù),用于處理有毒有害固體廢物,目前我國用于重金屬污染土壤修復(fù)的方法更多的是固化-穩(wěn)定化處理技術(shù),特別是對于重度的重金屬污染土壤的修復(fù)。為徹底解決企業(yè)搬遷后遺留場地的土壤污染問題,經(jīng)過多方案分析比較,采用了固化-穩(wěn)定化技術(shù)對該企業(yè)搬遷后的電鍍污染場地土壤進(jìn)行修復(fù)。經(jīng)處理后的土壤監(jiān)測結(jié)果可達(dá)到滿意的結(jié)果,為今后電鍍行業(yè)污染場地的土壤修復(fù)提供了可借鑒的方法,具有可參考的實(shí)際價值。
[Abstract]:According to the toxicity of heavy metals and the severity of pollution, the heavy metal prevention and control objects are divided into two categories. The first kind of heavy metal prevention and control objects are heavy metal elements such as lead, mercury, cadmium, chromium and metalloid arsenic. The second kind of prevention and control objects are thallium, manganese, nickel, zinc, copper and so on. This is also the principle of prevention and control stipulated by the Ministry of Environmental Protection in the 12th Five-Year Plan for Comprehensive Prevention and Control of heavy Metal pollution. At present, the State Environmental Protection Administration implements a strict total amount control system for heavy metal pollution emissions, and divides these polluted areas into key areas and non-key areas. Heavy metal soil pollution not only affects the ecological environment, but also has a serious impact on the safety of other environments. With the increase of urban population and the expansion of urban scale in our country, the new urban area planning requires the heavily polluted enterprises in the densely populated urban area to withdraw from the city and enter the park, and the factory area after relocation must carry out environmental impact assessment. The contaminated soil must be remedied before it can be used as the new use of urban land, so it is particularly important to restore the soil in the polluted site after the removal of the city and the relocation of the enterprise. The prevention and treatment of heavy metal pollution and soil remediation in soil has become an important research content of environmental protection workers. In this paper, heavy metal contaminated sites of electroplating enterprises after relocation are taken as the research object of soil remediation. In order to standardize the pollution caused by pollutants discharged from electroplating industry, further integrate all kinds of resources and give full play to the concentrated construction of electroplating industry. To control the advantages of scale and radiation, to ensure the healthy and stable development of electroplating industry, the electroplating production line of a certain high voltage switch company in Shandong Province should be relocated as a whole, according to the local urban planning and environmental protection requirements, The plant has now moved to the planned chemical industrial park. The contaminated soil of the original site needs to be remedied, and the contaminated soil of the original site needs to be repaired, with an area of about 7452 m2. Before the relocation of the enterprise to produce various types of electrical components as products, the production process needs a large number of electroplating links, electroplating elements involved in heavy metals chromium, copper, zinc; The site was planned for commercial use after relocation. The main target of remediation of contaminated site was the third grade standard value of soil Environmental quality Standard (GB15618-1995). The results showed that the maximum concentration of hexavalent chromium in contaminated soil was 41.7 mg / kg, the maximum concentration of total chromium was 4150 mg / kg Cu, the maximum concentration of zinc was 2220 mg / kg ~ (-1) mg 路kg ~ (-1), the maximum concentration of Cr ~ (6 +) was 5020 mg / kg ~ (-1) 路kg ~ (-1), the maximum concentration of Cr ~ (6 +) was 41.7 mg / kg ~ (-1). It far exceeds the third grade limit of soil Environmental quality Standard (GB15618-1995). Developed countries, such as Europe, America and Japan, have used the solidified and stabilized disposal technology (S / S process) as a commonly used restoration technology for the treatment of toxic and harmful solid wastes. At present, the remediation methods of heavy metal contaminated soils in China are more solidified and stabilized, especially for heavy metal contaminated soils. In order to thoroughly solve the problem of soil pollution of the site left behind after the relocation of the enterprise, through the analysis and comparison of many schemes, the soil of electroplating contaminated site after the relocation of the enterprise was remedied by using solidification-stabilization technology. The results of soil monitoring after treatment can reach satisfactory results, which provides a reference method for soil remediation of contaminated sites in electroplating industry in the future, and has practical value for reference.
【學(xué)位授予單位】:山東大學(xué)
【學(xué)位級別】:碩士
【學(xué)位授予年份】:2017
【分類號】:X53;X781.1

【參考文獻(xiàn)】

相關(guān)期刊論文 前10條

1 許石豪;張帥;胡林潮;;電鍍場地重金屬污染土壤穩(wěn)定化修復(fù)工程應(yīng)用研究[J];廣東化工;2017年01期

2 王加華;張峰;馬烈;;重金屬污染土壤穩(wěn)定化修復(fù)藥劑研究進(jìn)展[J];中國資源綜合利用;2016年02期

3 王文坦;李社鋒;朱文淵;黃凰;徐秀英;覃慧;宋自新;;我國污染場地土壤修復(fù)技術(shù)的工程應(yīng)用與商業(yè)模式分析[J];環(huán)境工程;2016年01期

4 吳舜澤;孫寧;盧然;趙云皓;王兆蘇;;重金屬污染綜合防治實(shí)施進(jìn)展與經(jīng)驗(yàn)分析[J];中國環(huán)境管理;2015年01期

5 金一凡;周連杰;杰克;葉旭明;;污染土壤修復(fù)技術(shù)的探討[J];環(huán)境科技;2012年05期

6 本刊編輯部;柳斌;;加強(qiáng)電鍍行業(yè)污染防治 規(guī)范電鍍行業(yè)有序發(fā)展——2012年部分電鍍園區(qū)整治提升工作掃描[J];表面工程資訊;2012年04期

7 李廣云;曹永富;趙書民;張楠;郭建民;張婷;趙瑩;;土壤重金屬危害及修復(fù)措施[J];山東林業(yè)科技;2011年06期

8 曹心德;魏曉欣;代革聯(lián);楊永亮;;土壤重金屬復(fù)合污染及其化學(xué)鈍化修復(fù)技術(shù)研究進(jìn)展[J];環(huán)境工程學(xué)報;2011年07期

9 郝漢舟;陳同斌;靳孟貴;雷梅;劉成武;祖文普;黃莉敏;;重金屬污染土壤穩(wěn)定/固化修復(fù)技術(shù)研究進(jìn)展[J];應(yīng)用生態(tài)學(xué)報;2011年03期

10 朱蘭保;盛蒂;;重金屬污染土壤生物修復(fù)技術(shù)研究進(jìn)展[J];工業(yè)安全與環(huán)保;2011年02期

相關(guān)會議論文 前2條

1 胡玲;鄭川;李琳;彭進(jìn)進(jìn);;典型電鍍污染場地土壤調(diào)查研究[A];2013中國環(huán)境科學(xué)學(xué)會學(xué)術(shù)年會論文集(第四卷)[C];2013年

2 常江;杜艷;姚艷娟;;安徽省主要土壤鉛含量及其與小麥幼苗生長相關(guān)性研究[A];土肥水資源高效利用與農(nóng)業(yè)面源污染防控技術(shù)研討會論文集[C];2011年

相關(guān)重要報紙文章 前1條

1 王肇嘉;;利用水泥窯協(xié)同處置工業(yè)廢棄物技術(shù)淺論[N];中國建材報;2011年

,

本文編號:2357865

資料下載
論文發(fā)表

本文鏈接:http://sikaile.net/kejilunwen/huagong/2357865.html


Copyright(c)文論論文網(wǎng)All Rights Reserved | 網(wǎng)站地圖 |

版權(quán)申明:資料由用戶6477b***提供,本站僅收錄摘要或目錄,作者需要刪除請E-mail郵箱bigeng88@qq.com
欧美日韩综合在线精品| 国产成人精品在线播放| 亚洲精品av少妇在线观看| 亚洲中文字幕日韩在线| 亚洲专区一区中文字幕| 日韩国产亚洲欧美另类| 99久久精品免费精品国产| 日本不卡一本二本三区| 亚洲日本韩国一区二区三区| 91在线国内在线中文字幕| 亚洲乱码av中文一区二区三区| 亚洲精品一二三区不卡| 国产又大又黄又粗的黄色| 欧洲日韩精品一区二区三区| 不卡中文字幕在线视频| 国产伦精品一一区二区三区高清版| 91免费一区二区三区| 91人妻人澡人人爽人人精品| 中文文精品字幕一区二区| 日韩精品一级一区二区| 老司机精品视频在线免费看 | 在线观看中文字幕91| 欧美日韩国产黑人一区| 亚洲另类欧美综合日韩精品 | 久久99精品国产麻豆婷婷洗澡 | 大香伊蕉欧美一区二区三区| 亚洲欧美一二区日韩高清在线| 午夜福利网午夜福利网| 大伊香蕉一区二区三区| 九九久久精品久久久精品| 色婷婷视频免费在线观看| 精品少妇一区二区视频| 丰满的人妻一区二区三区| 不卡中文字幕在线视频| 欧美三级精品在线观看| 久久永久免费一区二区| 91香蕉国产观看免费人人| 亚洲超碰成人天堂涩涩| 精品欧美日韩一区二区三区| 国产香蕉国产精品偷在线观看| 国产原创中文av在线播放|