环境工程学报
環境工程學報
배경공정학보
CHINESE JOURNAL OF ENVIRONMENTAL ENGINEERING
2010年
4期
915-918
,共4页
张厚坚%王兴润%陈春云%王琪%杨彦%永生青
張厚堅%王興潤%陳春雲%王琪%楊彥%永生青
장후견%왕흥윤%진춘운%왕기%양언%영생청
高原%铬渣%污染场地%污染特性
高原%鉻渣%汙染場地%汙染特性
고원%락사%오염장지%오염특성
plateau section%chrome residue%contaminated sites%polluting property
在我国高原地区某铬渣污染场地进行钻孔取样,分析场地工程地质特性,对场地铬的污染状况及空间分布特征进行研究.结果表明:场地地质结构较单一,地下水丰富,土质的渗透性强,渗透系数在1.78×10~(-3)~0.243 cm/s之间;场地铬污染严重,总铬与六价铬的浓度最大值分别为22485.6 mg/kg和7495.2 mg/kg,地下水中六价铬的浓度最大值为107.2 mg/L;通过剖面铬浓度分析:铬在纵向上浓度分布受土壤质地的影响,均呈现表层4m浓度较高,4m以下浓度较低且变化较小的规律.由Kriging插值法绘的铬浓度分布等值线图可清晰看出场地表层土表现出向沟谷位置迁移趋势,地下水中残留的铬向地下水流场方向迁移.
在我國高原地區某鉻渣汙染場地進行鑽孔取樣,分析場地工程地質特性,對場地鉻的汙染狀況及空間分佈特徵進行研究.結果錶明:場地地質結構較單一,地下水豐富,土質的滲透性彊,滲透繫數在1.78×10~(-3)~0.243 cm/s之間;場地鉻汙染嚴重,總鉻與六價鉻的濃度最大值分彆為22485.6 mg/kg和7495.2 mg/kg,地下水中六價鉻的濃度最大值為107.2 mg/L;通過剖麵鉻濃度分析:鉻在縱嚮上濃度分佈受土壤質地的影響,均呈現錶層4m濃度較高,4m以下濃度較低且變化較小的規律.由Kriging插值法繪的鉻濃度分佈等值線圖可清晰看齣場地錶層土錶現齣嚮溝穀位置遷移趨勢,地下水中殘留的鉻嚮地下水流場方嚮遷移.
재아국고원지구모락사오염장지진행찬공취양,분석장지공정지질특성,대장지락적오염상황급공간분포특정진행연구.결과표명:장지지질결구교단일,지하수봉부,토질적삼투성강,삼투계수재1.78×10~(-3)~0.243 cm/s지간;장지락오염엄중,총락여륙개락적농도최대치분별위22485.6 mg/kg화7495.2 mg/kg,지하수중륙개락적농도최대치위107.2 mg/L;통과부면락농도분석:락재종향상농도분포수토양질지적영향,균정현표층4m농도교고,4m이하농도교저차변화교소적규률.유Kriging삽치법회적락농도분포등치선도가청석간출장지표층토표현출향구곡위치천이추세,지하수중잔류적락향지하수류장방향천이.
Through drill hole sampling in a chromium slag contaminated site in plateau section of China,the engineering geological characteristics, Cr pollution and spatial distribution of the site were studied. The results showed that the site had a simplex geological structure, abundant ground water, a high permeability of soil,and the field coefficient of permeability ranged from 1.78 × 10~(-3) cm/s to 0. 243 cm/s. The space was seriously polluted by Cr. In soil, the maximum concentration of total Cr was 22485.6 mg/kg, that of Cr (VI) was 7495.2 mg/kg, and in the ground water, that of Cr(VI) was 107.2 mg/L. The content of Cr in the soil section showed that it had the highest concentration at 4 m under ground, but at the lower soil it was lighter, and had little change. This distribution pattern was related with the soil texture. It was found that Cr was transported to the valley floor in the topsoil, and the transport of the pollutant in the ground water was towards the groundwater flow field form the Cr concentration contour map whieh was drawn by Kriging' s method of interpolation.