稠化酸返排液深度处理试验研究

针对陕北某气井稠化酸返排液pH值低、SS高、COD高、矿化度高和透光率低的特点,提出采用微电解-Fenton联合工艺处理稠化酸返排液,以期达到降低返排液COD,为后续混凝和活性炭吸附处理提供有利条件。试验结果表明:在铁屑20g、活性炭15g、H_2O_2 900mg/L,微电解-Fenton联合处理2h;调节pH值至7.5左右,PAC 700mg/L、PAM 50mg/L,混凝处理30min;活性炭40g/L,活性炭吸附处理40min的条件下,处理后的稠化酸返排液pH值为7.50、SS降至15mg/L、COD降至109.3mg/L、透光率提高至99.5%,水质达到GB 8978—1996《污水综合排放标准》二级标准。     

钻井污水处理的物化工艺研究

对二级化学混凝、Fenton氧化与微孔膜过滤耦合技术工艺处理钻井污水进行了实验研究。首先通过对不同混凝剂的对比实验，确定了最佳混凝剂及试剂最佳投加量，探讨了耦合条件对处理出水COD的去除效果。实验结果表明，采用PAC和PFS的二级混凝、Fenton氧化与微孔膜过滤耦合技术工艺可使钻井污水COD去除率达到95％，其余各项指标亦达标。     

混凝沉降-微电解-催化氧化法处理钻井废水

采用混凝沉降-微电解-催化氧化法对钻井废水进行处理,筛选出最佳的工艺条件。实验结果表明,该法可使原水的CODCr从5846 mg/L降至150 mg/L以下,色度去除率达到100%,出水达到排放标准。混凝沉降-微电解-催化氧化法对于处理高CODCr、高色度钻井废水是行之有效的,具有广阔的应用前景。     

套管保护液对钻井废水处理效果的影响＊

通过研究高含硫气田钻井完井后套管保护液对钻井废水处理效果的影响,可知:采用混凝/二次絮凝/吸附工艺处理不含套管保护液的钻井废水时,出水COD<150 mg/L;当套管保护液加量>0.5 mL/L时,出水中COD随套管保护液用量增加而急剧升高,远大于150 mg/L;采用混凝/吸附/微电解组合工艺处理含套管保护液的完井钻井废水,出水COD<150 mg/L,满足GB 8978-1996《污水综合排放标准》二级标准的要求。     

含硝基苯、苯胺废水处理的工程实践

采用固定化微生物-曝气生物滤池与铁-炭微电解法联用的工艺方法处理含硝基苯、苯胺的废水。通过培养驯化微生物阶段、半负荷进水阶段、满负荷进水阶段的调试运行,表明:当进水CODCr<1 000mg/L、硝基苯<120mg/L、苯胺<30mg/L时,出水可达到CODCr<300mg/L、硝基苯<5mg/L、苯胺<5mg/L的设计要求。铁-炭微电解法在pH值为3～4时,对废水有一定的脱色作用,但pH值升高后脱色效果不明显。     

高含盐钻井废水真空蒸发处理实验

针对钻井过程产生的高含盐废水和反渗透处理产生的高含盐水的特点,采用混凝预处理、过滤、真空蒸发处理工艺对钻井废水进行综合处理,混凝实验探讨了混凝剂(PAC)、助凝剂(PAM)、pH值、静置时间和搅拌速度对CODCr去除率的影响,得出混凝实验最佳方案。并对过滤实验、蒸发实验结果进行分析。实验表明:混凝预处理、过滤后的废水再进行真空旋转蒸发处理,馏出液经冷却收集后能达到GB 8978—1996《污水综合排放标准》一级标准,实验可为高含盐废水处理工艺提供参考。     

油田钻修井废水处理工艺技术研究及应用

在钻井、完井、井下作业等油气田开发生产过程中,会产生钻井泥浆压滤液、压井液、洗井液、压裂和酸化返排液等含油钻修井废水,这些废水组成复杂难处理,无法直接外排或回注。文章对冀东油田钻修井废水的水质特性及组成进行分析,开发了1套钻修井废水一体化处理技术,介绍了电催化、絮凝沉降、铁碳微电解、多级砂滤等核心工艺,开展了絮凝剂、助凝剂及pH值调节剂的最佳条件试验研究。研究结果表明:最佳药剂添加浓度分别为絮凝剂50 mg/L、助凝剂6 mg/L,最佳絮凝效果反应条件pH值为9。同时,现场试验应用结果表明:该工艺处理后的污水水质能够达到SY/T 5329—2012《碎屑岩油藏注水水质指标及分析方法》相关指标要求,实现了钻修井废水的合规化处置。     

JZW-4钻井污水处理装置的研制及应用

为解决现有的钻井污水处理设备无法满足污水处理需要的问题,研制了ＪＺＷ－４型钻井污水处理装置。对污水进行了室内试验,证明只有混凝－离心－过滤法是最佳的处理方法;并根据此方法研究制造出了ＪＺＷ－４钻井污水设备。现场试验结果表明：用该装置处理污水,出口水质符合国家综合二级排放标准。说明ＪＺＷ－４钻井污水处理装置工艺流程设计合理,适应性强,处理效果好,具有创造性。     

炼油污水深度处理回用工艺实验研究

试验工艺流程的方案选定,充分吸收了各炼油厂进行的污水深度处理的成功试验经验,以原臭氧生物活性炭工艺单元为基础,提出了以混凝气浮与臭氧生物活性炭串联工艺为核心的总体工艺流程,以降低工程投资及处理成本,提高污水回用的经济效益;同时,指出试验过程中所存在的问题及其对策。因此,开展炼油污水深度处理回用工艺试验研究,必将为炼油污水深度处理提供强有力的技术支撑,可作为相关污水回用处理工艺选择的参考。     

化学氧化—混凝沉淀法处理油田作业废液

采用化学氧化—混凝沉淀法对油田作业废液进行处理,筛选出最佳的混凝条件及氧化条件。实验结果表明,与产出水混合处理后可使原水的悬浮物从500～1000 mg/L降至<3 mg/L、总铁<0.5 mg/L。处理后的污水由处理前的黑浆状变为清澈透明,淡黄色,基本达到了注水水质标准。该方法具有投资小、净化效果好、设备简单、占地面积小、操作方便、不产生二次污染等优点。     

废旧铝、铁片粉煤灰复合混凝剂的制备及在废水处理中的应用

我国粉煤灰和铝、铁片固体废物产量日益增多,危害越来越严重。在高温加热、搅拌条件下,用强酸浸渍粉煤灰和易拉罐碎片,使粉煤灰和废旧铝、铁片资源化,制得废旧铝、铁片粉煤灰复合混凝剂,并用所制得的废旧铝、铁片粉煤灰复合混凝剂处理屠宰废水。在一定条件下,经混凝试验处理后的屠宰废水pH值在7左右,COD去除率为92．0％,SS去除率为98．7％,浊度去除率为98．4％,色度去除率为96．6％。结果表明,粉煤灰和废旧铝、铁片资源化和在废水处理中的应用具有可行性。     

用二级絮凝强化技术处理钻井污水研究

絮凝沉降法是国内外普遍采用的钻井污水处理方法。对辽河油田的钻井污水采用二次絮凝处理工艺进行了实验。该油田钻井污水处理中选用CaCl2作为一级絮凝剂,利用离心强化固液分离法,污染物的脱除效率高,处理时间短。用二级絮凝强化技术处理钻井污水时采用了调质剂C和助凝剂D与絮凝剂PAC或LX复配,出水中铬的化学需氧量低于150mg/L,处理后的水质满足排放标准。     

钻井污水与采油污水混合处理

中原油田产生的钻井污水的化学需氧量(COD)、矿化度、色度、悬浮物及含油量均比较高,直接外排将会对周边生态环境造成污染,与采油污水混合处理又将导致处理后的水质达不到标准,因而采用将钻井污水处理后再与采油污水混合的方法,这种混合污水进入采油污水处理系统的试验结果表明,处理后的钻井污水与采油污水配伍性良好,净化水无结垢倾向,处理后的净化水与杀菌剂、缓蚀剂相容性良好,其主要指标均达到部颁注水水质标准。     

厌氧-好氧工艺在含油废水生化处理中的应用

(中国石油冀东油田分公司安全环保处)论述了厌氧-好氧(A/O)工艺的基本原理及工艺参数。该工艺在冀东油田两座废水处理站的应用结果表明,对废水中石油类物质、COD、硫化物去除效果明显。高一联合站及柳一联合站污水经处理后,石油类物质去除率分别为90.6%和96.0%;COD去除率分别为86.0%和91.6%;硫化物去除率分别为94.8%和98.2%,处理后的污水均达到一级排放标准。另外,采用厌氧-好氧工艺的成本相对较低,处理费用低于0.5元/m3。处理后的污水若回注地下,平均费用为4.7元/m3。     

对铁碳处理硝基酚废水的研究

铁碳降解水中难降解有机污染物的影响因素、最佳工艺参数及处理效果;初步探讨了氧化降解污染物的作用机理;通过分析污染物降解的中间产物,提出了污染物降解的可能途径.探讨了pH、铁碳用量、温度以及锰矿物的粒径等对处理效果的影响,在最佳的工艺条件下,CODCr的去除率达到95%以上,TOC测定表明：大部分硝基酚被氧化降解为H2O和CO2.对硝基酚的降解途径主要是微电解将对硝基酚还原为对氨基酚,对氨基酚在酸性条件下被软锰矿氧化为H2O和CO2做探索性研究.     

Significance of iron compounds in chemical and electro‐oxidation treatment of sugar industry wastewater: Batch reaction

Industrialization plays a major role in a nation's growth. However, with an increase in industrial activities, pollution levels are also increasing. Among all industries, the sugar‐processing industry is one that requires large amounts of water to process the sugar, and, consequently, it discharges large amounts of water as effluent. Highly polluted wastewater brings changes to the physicochemical characteristics of the surrounding environment. Iron compounds have had a significant impact when they are used in wastewater treatment in various applications, including when they are used to minimize the pollution levels in sugar industry wastewater (SIWW). To minimize the pollutant levels from SIWW, iron compounds have been key for uses in treatments involving chemical and electro‐oxidation. Two different methodologies of electrocoagulation and chemical coagulation have been used to treat SIWW. In electrocoagulation, an iron plate is used as an electrode material under specific operating conditions. Ferrous sulfate and ferric chloride have been used as chemical coagulants at various pH and mass loading levels. The use of iron metals shows an 82% reduction in chemical oxygen demand (COD) and an 84% reduction in color at the optimum condition of pH 6, an electrode distance of 20 millimeters, and a current density of 156 square centimeters. As a chemical coagulant, iron salt (ferrous sulfate) provides a reduction of 77% COD and a 91% reduction of color at pH 6 and a 40‐millimole mass loading. Electrochemical treatment using iron was found to be suitable to treat SIWW. The sludge generated after treatment can be burned or composted with the possible recovery of some of the treatment costs.     

GOALS IN WASTEWATER TREATMENT1

Within a few years all domestic wastewater effluents in the United States will be subjected to a minimum of a properly operated primary and secondary treatment process. This implies a very high degree of removal of the more readily biologically degradable material as measured by the BOD test. This practice will to a large degree negate the value of the BOD test as a pollution parameter. Organic carbon appears to be a more suitable means for determining the strength of a wastewater or for controlling the operation of physical and chemical treatment processes. Studies were conducted to determine the effect of time of passage on the ratio of organic carbon to BOD, COD and carbohydrate. The ratio was found to vary with both time and the state of the sample. The carbon content was reduced to a lesser degree than the other parameters. Organic carbon content appears to correlate better with COD than with BOD. The efficiency of a chemical precipitation process can be determined on the basis of organic carbon removal.     

Magnetic composite prepared from palm shell-based carbon and application for recovery of residual oil from POME

Magnetic separation combined with adsorption by activated carbon has been found to be a useful method for removing pollutants. In this paper, the use of palm shell as a source of activated carbon for the removal and recovery of oil from palm oil mill effluent (POME) is studied. In the first part of the study, the properties of samples of activated carbon prepared from palm shell under a variety of different conditions were characterized for their hydrophobicity, surface areas and pore size distribution. The most effective of the activated carbon samples was prepared by impregnation with ZnCl(2) followed by combined physical/chemical activation under carbon dioxide flow at 800 °C. Four grams of these samples adsorbed 90% of the oil from 50 mL POME. In the second part, the palm shell-based carbon samples were given magnetic properties by the technique of iron oxide deposition. Ninety-four percent of the activated carbon/iron oxide composite containing the adsorbed oil could be extracted from the POME by a magnetic bar of 0.15 T. Four grams of the composite can remove 85% of oil from 50 mL POME and a total of 67% of the initial oil can then be recovered by hexane extraction. Powder X-ray diffractometry showed the presence of magnetite and maghemite in the activated carbon/iron oxide composite.     

Application of 'waste' wood-shaving bottom ash for adsorption of azo reactive dye

The utilization of wood-shaving bottom ash (WBA) for the removal of Red Reactive 141 (RR141), an azo reactive dye, was investigated. WBA/H(2)O and WBA/H(2)SO(4) were made by treating WBA with water and 0.1M H(2)SO(4), respectively, to increase adsorption capacity. Adsorption of RR141 from reactive dye solution (RDS) and reactive dye wastewater (RDW) by WBA/H(2)O and WBA/H(2)SO(4) involved the BET surface area and pore size diameter. Properties of adsorbents, effect of contact time, initial pH of solution, dissolved metals and elution studies indicated that the decolorisation mechanism involved both chemical adsorption and precipitation with calcium ions. In addition, the WBA/H(2)SO(4) surface might contain sulphate-cation complexes that were specific to enhancing dye adsorption from RDW. The adsorption isotherm had a best fit by the Freundlich model. Freundlich parameters showed that WBA/H(2)O used more heterogeneous surface than WBA/H(2)SO(4) and activated carbon for RDW adsorption. A thermodynamic study indicated that RDW adsorption was an endothermic process. The maximum dye adsorption capacities of WBA/H(2)O, WBA/H(2)SO(4) and activated carbon obtained from a Langmuir model at 30 degrees C were 24.3, 29.9, and 41.5mgl(-1), respectively. In addition, WBA/H(2)O and WBA/H(2)SO(4) could reduce colour and high chemical oxygen demand (COD) of real textile wastewater. According to the difficulty in the elution study, it was an environmentally safe disposal of this waste. Therefore, WBA, a waste from combustion of wood shavings, was suitable to be used as an effective adsorbent for azo reactive dye removal.