使用差压计测定低值BOD5

污水处理厂活性污泥经过洗涤后,在5 d的时间里其内源呼吸耗氧量线性较好,可以采用处于内源呼吸阶段的活性污泥作为BOD5测定的载体,一方面能够确保测定初期快速启动,另一方面能够提高测量范围,从而减小仪器的系统误差.活性污泥经过洗涤去除吸附的有机物后,将其制成浓度为200 mg/L左右的接种溶液用于低值BOD5测定,测量结果介于采用稀释法测定和差压计直接测定结果之间.当水中BOD5较低时,可以使用本方法进行测定,为测定低值BOD5提供一种新思路和新方法.     

Assessment of the Heavy Metal Pollution Effects on the Soil Respiration in the Baix Llobregat (Catalonia, NE Spain)

A main goal of investigations is to determine could a soilrespiration be an indicator of the soil pollution. In this case a measured levelof the soil oxygen consumption depends of its pollution. It alsomeans that the pollution reduces biological processes in edaphon.Investigated soil samples were taken from polluted andnon-polluted places in the Baix Llobregat near Barcelona (Catalonia, NE Spain). Soil samples were taken from the top ofsoil (0–5 cm) without a litter. Soil analysis were done, determining percentage shares of coarsefragments, coarse sand, fine sand, coarse silt, fine silt, clay,CaCO₃, organic matter as well as water pH and conductivityCE (1:5 [mS cm^-1]). Also were determined (in mg kg^-1)quantities of heavy metals, as Fe, Al, Mn, Zn, Cr, Ni, V, Cu, Cd, Pb.The soil respiration was investigated in temperatures15 and 30 °C and with controlled humidity.The respiration in 30 °C is number of times greater thenin 15 °C both for polluted and non-polluted soils.Particularly high coefficients of correlation between the soilrespiration and soil pollution in polluted soils were obtainedfor Pb: r = 0.75 in 15 °C and r = 0.98 in30 °C; for Ba: 0.90 and 0.57; for V: 0.99 and 0.81. In non-polluted soils highest correlation coefficients are for Pb: r = 0.70 in 15 °C; Fe: 0.60 and 0.72; Al: 0.68 and0.64; Mn: 0.51 and 0.66; Ba: 0.63 and 0.61; Cr: 0.94 and0.70; Ni: 0.64 and 0.65; Cu: 0.69 and 0.48; as well as V: 0.62in 15 °C; and Cd: 0.69 in 15 °C.This way the soil respiration could be a good indicator of the soil pollution.     

ASM1中废水和污泥组分浓度的测定方法研究

对呼吸计量法应用于校准ASM1作了简明的阐述。在呼吸速率与模型组分关系的基础上,介绍了ASM1中废水与污泥各组分浓度的测定方法,并指出模型组分细化的意义。     

活性污泥数学模型中进水易降解有机物的测定

ASM系列模型 (ASMs)自推出以来在欧美得到广泛应用。要想利用ASMs对特定污水处理过程进行准确的模拟 ,首先必须得到该过程污水的水质特性参数。介绍了连续式OUR计量法、序批式OUR计量法和絮凝过滤物理化学法等 3种测定ASMs中进水易降解有机物的方法 ,通过分析比较指出了各自的优缺点及适用情况。     

COD组分分析的实验条件及结果可靠性分析

本研究尝试用SF(OURmax/OURen)代替S(0)/X(0)来作为呼吸法确定COD组分最优实验条件的参数,从而简化测量过程且可实现自动化操作.另外由生长消耗COD与生物量的比值来判断测量结果的可靠性.结果表明,获得可靠的RBCOD组分分析结果的实验条件为:1对于易生物降解含量较高的水质(如由乙酸钠配制的污水),SF在2.8~5.3范围内,生长消耗COD与生物量比值在30%以内;2对于易生物降解和难生物降解物质适中的水质(如典型生活污水),SF应在5.8~6.4左右,生长消耗COD与生物量比值在30%以内;3而对于含有大量难生物降解物质的工业废水(垃圾渗滤液),SF在15以下,且生长消耗COD与生物量的比值在40%以内.由此可见,采用呼吸法确定COD组分,其最优条件SF范围随碳源的复杂程度的上升而上升.     

蛋白泡沫灭火剂及其组分的生物降解试验

采用呼吸计量法考察蛋白泡沫灭火剂组分对其降解性的影响,明确几种国内典型蛋白泡沫灭火剂的生物降解性能。20 d快速生物降解试验结果表明:水解蛋白浓缩液易于生物降解,防腐剂苯酚的添加不会抑制蛋白泡沫灭火剂的生物降解,泡沫稳定剂硫酸亚铁则会对蛋白泡沫灭火剂的生物降解有所影响;6种市售典型蛋白泡沫灭火剂的20 d生物降解率均超过60%,抗溶型蛋白泡沫灭火剂的生物降解性普遍较高;国内蛋白泡沫灭火剂产品的20 d生物降解率远高于国外同类产品,在生物降解性能方面比国外同类产品更具有优势。     

应用呼吸-滴定测量监测硝化动态过程

将pH值在线监测与药品自动投加系统与已开发的混合呼吸测量仪集成,组成自动呼吸-滴定测量仪,同时测定废水生物处理过程氧气利用速率(OUR)和质子变化速率(HVR).对活性污泥硝化过程定时测定NH4+-N浓度,比较其与基于HVR或OUR预测的NH4+-N浓度间的一致程度,评估自动滴定测量装置测试硝化过程动态的性能.结果表明,在初始NH4+-N浓度分别为20,25mg/L的间歇试验中,实测值数组与基于OUR的预测值数组间的相关系数分别为0.9967和0.9972,与基于HVR的预测值数组间的相关系数分别为0.9991和0.9992,表明OUR和HVR均能及时准确地反映硝化过程的动态特性.     

基于ASM2的快速易生物降解COD组分表征方法构建

基于活性污泥2号模型（ASM2）对快速易生物降解组分（SS）进一步划分为可发酵的易生物降解有机物（SF）和发酵产物（SA）,本研究提出了一套科学的表征方法。该方法涉及SS与XS（慢速可生物降解组分）的好氧呼吸测量同时表征、SA组分的离子色谱测定以及物料衡算。应用这套方法对重庆市某2个城市污水厂隔栅井出水水样平行进行了4组实验,各种组分测量值序列的CV值在2.09%～6.18%之间。     

A respirometric method to measure mineralization of polymeric materials in a matured compost environment

A respirometric method was developed to measure the mineralization of polymeric materials in a matured compost environment. For the purpose of evaluating the method, results obtained for the mineralization of glucose and cellulose are presented. The matured compost, in addition to supplied nutrients, micronutrients, and an inoculum, serves as the matrix which supports the microbial activity. Recovery of the substrate carbon in the form of carbon dioxide from the glucose and cellulose added to test vessels was 68 and 70%, respectively. A statistical evaluation of the results obtained on substrate mineralization was carried out and showed acceptable reproducibility between replicate test vessels and test runs. The testing protocol developed has the following important characteristics: (1) the test reactors are maintained at 53 °C at a high solids loading (60% moisture), which has certain characteristics that are similar to a thermophilic compost environment; (2) the test matrix providing microbial activity is derived from readily available organic materials to facilitate reproducibility of the method in different laboratories; (3) the equipment required to perform this test is relatively inexpensive; and (4) the information obtained on polymer mineralization is vital to the study and development of biodegradable polymeric materials.Guest Editor: Dr. Graham Swift, Rohm & Haas.     

Dialdehyde starch and zein plastic: Mechanical properties and biodegradability

Dialdehyde starch (DAS) and zein, a hydrophobic corn protein, were investigated to produce biodegradable plastics with improved water resistance and mechanical properties. In the study, dialdehyde starch and zein ratio, plasticizers, and degree of starch oxidation were examined. Increased molding temperature and level of starch oxidation decreased water absorption of the plastic. Tensile strength and Young's modulus increased with starch oxidation. The biodegradation of starting materials and ground plastic specimens was studied in aerobic soil reactors maintained at 25°C for 180 days. Biodegradation of corn starch, zein, and dialdehyde starch for 180 days produced CO₂ equivalent to 64, 63, and 10% of theoretical carbon, respectively. Specimens of molded DAS and zein (3 : 1) plastic showed accelerated CO₂ evolution compared to DAS and other raw materials alone. By 180 days, specimens made with starch of low oxidation (1 and 5% oxidized) demonstrated a 60% biodegradation, and specimens with highly oxidized starch (90% oxidized) achieved 37% biodegradation.Paper presented at the Bio/Environmentally Degradable Polymer Society—Third National Meeting, June 6–8, 1994, Boston, Massachusetts.Journal Paper J-15927 of the Iowa Agriculture and Home Economics Experiment Station, Ames, Project No. 3258.