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1)  Deposition and purification
沉淀纯化
2)  chemical sedimentation
化学沉淀
1.
On the basis of the basic principle of chemical sedimentation process, the chemicalsedimentation process that treats sulphide in acetylene sludge wastewater using FeSO.
根据化学沉淀法的基本原理,提出了利用FeSO4及盐泥(工业废料)为药剂的化学沉淀法处理电石渣浆废水中硫化物的处理方法。
3)  chemical precipitation
化学沉淀
1.
Recovery of magnesium ammonium phosphate from ammonia nitrogen wastewater by chemical precipitation;
化学沉淀法从氨氮废水中回收磷酸铵镁
2.
Production of ZnS from flue gas SO_2 through the combined processes of microbial transformation and chemical precipitation;
用微生物转化-化学沉淀法从烟气SO_2中制取ZnS
3.
Mathematical model for treating electroless nickel plating wastewater by chemical precipitation and its application;
化学沉淀法处理化学镀镍废水的数学模型及应用
4)  physico-chemical precipitation
物化沉淀
5)  precipitation strengthening
沉淀强化
1.
Influence of high temperature aging on precipitation strengthening of Ni-based superalloy;
高温时效对高温镍基合金沉淀强化的影响
2.
The industrial trial that rolling 590 MPa grade automobile beam steel by using of 510 MPa grade billet was carried out,and the rolling process principles of improving performance through grain refining and precipitation strengthening for V-microalloyed steel was analyed.
在攀钢1450热连轧生产线进行了利用510 MPa级化学成分的钢坯轧制590 MPa级汽车大梁钢的工业试验,分析了钒微合金钢通过晶粒细化和沉淀强化提高性能的工艺原理。
3.
Results show that such kind of alloy, after aging treatment at 450 ℃ for 4 hours, can reach the maximum strength, and Cr will influence the property of alloy by precipitation strengthening.
结果表明 :该合金 45 0℃ 4h时效处理 ,其强度达最大值 ,Cr对合金性能的影响是通过沉淀强化来实现的 ,并对该合金沉淀强化机制的定量关系进行了探
6)  chemical deposition
化学沉淀
1.
SO42-was removed by the chemical deposition techniques,and COD was then removed by the batch Anaerobic Hydrolysis-acidogenesis-Aerobic biotechnology which was performed under different influent organic loads adjusted by changing HRT and MLSS.
方法利用化学沉淀法去除部分SO42-,然后利用序批式厌氧水解酸化-好氧生物实验对其中的COD进行去除,通过改变水力停留时间(HRT)和菌浓度(MLSS)调整进水生物负荷,根据生物去除负荷及出水情况分析进水生物负荷对处理效果的影响。
2.
Pilot scale and lab scale experiments were conducted to pretreat the ion exchange wastewater (the main part of the monosodium L glutamate (MSG) wastewater) by means of Fe C deoxidization to increase the pH and biodegradation, lime counteraction and aeration by air or chemical deposition to remove ammonia.
采用铁碳法、吹脱法和化学沉淀法对味精废水中离交废水的预处理进行了中试和小试。
3.
The paper introduced the method and the theory of Lead Sulfide film preparation——Chemical Deposition and analyzed the reason of outshoot cling to the surface of Lead Sulfide film during the process of chemical deposition.
本文介绍了PbS薄膜常用化学沉淀的制备方法及原理,深入分析了基片沉淀过程中表面出现突出物现象的原因,薄膜基片电镜分析以及改善PbS基片表面均匀性的工艺方法。
补充资料:DCZc系列氮气纯化设备

 

技术指标:
纯度≥99.9995%
露点≤-70℃
氧含量≤5ppm
氢含量≤1ppm 
特点:
原料气氧含量小于1000ppm时,使用高效脱氧剂除氧,氮气纯度和压力不受氢气影响。 

DCZc氮气纯化设备工作原理图 
 



型号规格

额定处理气量
有效供气量
耗氢量
装机功率
使用功率
冷却水
Nm3 /h
Nm3/h
Nm3/h
kw
kw
T/h
DCZc-10
11
10
0.028
2
1.0
0.9
DCZc-20
22
20
0.06
4
2.0
1.5
DCZc-40
44
40
0.11
8
4.0
3.5
DCZc-60
66
60
0.17
12
6.0
5.5
DCZc-80
88
80
0.22
16
8.0
7.0
DCZc-100
110
100
0.28
21
10.5
9.0
DCZc-120
132
120
0.33
25
12.5
10.5
DCZc-150
165
150
0.40
31
15.5
13.5
DCZc-180
198
180
0.50
37
18.5
16.0
DCZc-200
220
200
0.55
42
21.0
18.0
DCZc-250
275
250
0.69
52
26.0
22.5
DCZc-300
330
300
0.83
63
31.5
27.0
DCZc-350
385
350
0.96
73
36.5
31.0
DCZc-400
440
400
1.10
84
42.0
36.0
DCZc-450
495
450
1.25
94
47.0
40.5

注:本表所列数据以20℃环境温度,0米标高,80%相对湿度,设备进口氮气纯度为99.5%, 25℃冷却水温度为设计基准。

瑞安市耀星气体净化器材有限公司 
地址:浙江省瑞安市塘下镇新陈东路137号 
电话:0577-65396358 
传真:0577-65396398 
说明:补充资料仅用于学习参考,请勿用于其它任何用途。
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