广州化工
廣州化工
엄주화공
GUANGZHOU CHEMICAL INDUSTRY AND TECHNOLOGY
2015年
4期
68-70
,共3页
傅慧萍%林雅婷%缪韵娜%李娜丽%黄晓东
傅慧萍%林雅婷%繆韻娜%李娜麗%黃曉東
부혜평%림아정%무운나%리나려%황효동
牡蛎壳%铜%过硫酸钠%酸性红FRL
牡蠣殼%銅%過硫痠鈉%痠性紅FRL
모려각%동%과류산납%산성홍FRL
oyster shell%copper%sodium persulfate%acid red FRL
以牡蛎壳为载体,采用超声浸渍法-焙烧制备牡蛎壳负载铜的催化剂,利用电镜扫描(SEM)、 X射线衍射(XRD)对催化剂进行表征。以酸性红FRL为降解目标物,研究此催化剂催化过硫酸钠降解酸性红FRL的性能。考察了催化剂焙烧的条件、氧化剂浓度、催化剂用量和初始染料浓度对降解的影响。结果表明,催化剂经500℃焙烧3 h,催化活性较高;当初始污染物浓度为120 mg·L-1,氧化剂浓度为0.28 g·L-1,催化剂用量为0.70 g·L-1时,降解2.5 h,酸性红FRL染料溶液的降解率可达80.3%以上。
以牡蠣殼為載體,採用超聲浸漬法-焙燒製備牡蠣殼負載銅的催化劑,利用電鏡掃描(SEM)、 X射線衍射(XRD)對催化劑進行錶徵。以痠性紅FRL為降解目標物,研究此催化劑催化過硫痠鈉降解痠性紅FRL的性能。攷察瞭催化劑焙燒的條件、氧化劑濃度、催化劑用量和初始染料濃度對降解的影響。結果錶明,催化劑經500℃焙燒3 h,催化活性較高;噹初始汙染物濃度為120 mg·L-1,氧化劑濃度為0.28 g·L-1,催化劑用量為0.70 g·L-1時,降解2.5 h,痠性紅FRL染料溶液的降解率可達80.3%以上。
이모려각위재체,채용초성침지법-배소제비모려각부재동적최화제,이용전경소묘(SEM)、 X사선연사(XRD)대최화제진행표정。이산성홍FRL위강해목표물,연구차최화제최화과류산납강해산성홍FRL적성능。고찰료최화제배소적조건、양화제농도、최화제용량화초시염료농도대강해적영향。결과표명,최화제경500℃배소3 h,최화활성교고;당초시오염물농도위120 mg·L-1,양화제농도위0.28 g·L-1,최화제용량위0.70 g·L-1시,강해2.5 h,산성홍FRL염료용액적강해솔가체80.3%이상。
The copper-loaded oyster shells as catalysts were prepared through ultrasonic impregnation-calcination and were characterized by scanning electron microscope ( SEM) and X-ray powder diffraction ( XRD). The degradation performance by persulfate was investigated through the catalyst with acid red FRL as targeted pollutant. The effects of the factors, such as calcination conditions, concentration of oxidant, dosage of catalyst and initial concentration of pollutants were studied. The results showed that catalyst could have good activity after being heated for 3 h at 500 ℃. The removal rate of acid red FRL could reach 80.3% after 2.5 h under certain conditions: initial concentration of acid red FRL of 120 mg·L-1 , concentration of oxidizing agent of 0.28 g·L-1 , catalyst dosage of 0.70 g·L-1 .