Utility of risk-time curves in selecting remediation alternatives

The basis for risk-time curves associated with remediation of hazardous waste sites is developed. The utility of the risk-time curves as a part of a methodology for selecting between alternative remediation schemes is demonstrated when the time-frames for remediation are different for different alternatives. The potential for inclusion of uncertainty aspects in risk-time curves is considered.     

A Review of the Status of Advanced Technologies for the Detection of Oil in and with Ice

Remote sensors for application to oil in ice and oil with ice are assessed. Radio-frequency methods to detect oil in ice depend on the difference in dielectric properties between oil and water. Freshwater ice is relatively transparent to frequencies below about 200 MHz. Despite extensive theoretical studies, there is a lack of experimental evidence to support the notion that radio-frequency methods have potential.Acoustic methods for the detection of oil in ice show promise. Regular metal inspection equipment is capable of detecting oil layers under ice. Oil propagates shear waves and detection methods based on this unique property are capable of identifying oil in ice. One unit has been built and tested in the field based on this principle.Oil with ice detection is a well developed technology. A common sensor is an infrared camera or an IR/UV (infrared/ultraviolet) system. The inherent weaknesses include the inability to discriminate oil on beaches, among weeds or debris. The laser fluorosensor is a most useful instrument because of its unique ability to identify oil on backgrounds that include water, soil, ice and snow. It is the only sensor that can positively discriminate oil on most backgrounds. Radar offers the only potential for large area searches and foul weather remote sensing, however, there is little potential to detect oil in the immediate vicinity of ice. A major weakness of radar is that it is limited to operation over seas with winds of about 2–8 m/s.Equipment operating in the visible region of the spectrum, such as cameras and scanners, is useful for documentation or providing a basis for the overlay of other data. It is not useful beyond this because oil shows no spectral characteristics in the visible region that can be used to discriminate oil.     

内标法与外标法测定废气中挥发性有机化合物

目前采用热脱附-气相色谱-质谱法测定废气中挥发性有机化合物时多使用外标法。实验对比了内标法与外标法测定时存在的差异,发现大多数VOCs内标法的回收率均高于外标法,且内标法的相对标准偏差普遍小于外标法,内标法测定的准确度和精密度均优于外标法。内标法的标准曲线可使用更长时间,对于大量样品的测定非常有利;而外标法必须每次测定时重新绘制新曲线。故废气中VOCs测定工作推荐使用内标法定量。     

环境治理工程评标的双基点模型及应用

动用多指标综合排序的双基点法，建立了环境治理工程评标的数学模型。应用实例表明，该模型可以为环境治理工程评标提供客观、合理的方法。     

阻尼降噪材料的研究进展

阻尼降噪材料作为一类功能环保材料,因其优越的减振、抗冲击、隔噪声性能而获得广泛应用,介绍了阻尼降噪材料的作用机理,综述了聚合物基阻尼降噪材料、金属类阻尼降噪材料、阻尼降噪复合材料及其他阻尼降噪材料的研充进展,分析了阻尼降噪材料住未来的发展趋势。     

炼化企业SO2减排潜力分析

介绍了炼化企业的SO2排放源,建立了自备电厂SO2减排量数学模型,研究了SO2减排量对各影响因素的敏感度,分析了炼化企业SO2减排潜力.自备电厂燃煤锅炉SO2减排措施包括:增设脱硫设施,改进现有脱硫工艺,提高脱硫效率;关停小机组;降低燃料中硫含量.生产过程中催化裂化催化剂再生烟气的脱硫减排措施包括:降低原料硫含量;使用...     

头孢类抗生素生产废水污染与处理现状

分析了头孢类抗生素生产废水的污染现状,指出了废水的来源及主要特征.介绍了目前常用的头孢类抗生素废水处理技术:物化处理技术和生物处理技术,其中厌氧(缺氧)-好氧组合工艺是处理高浓度头孢类抗生素废水的主要方法,提出了头孢类抗生素企业的污染防治对策.     

Processing of Egyptian boiler-ash for extraction of vanadium and nickel

Proposed technique in this investigation is given for vanadium and nickel enrichment in the Egyptian boiler ash. Among the various concepts for recovery of vanadium and nickel from boiler ash, the pyro-metallurgical approach is technically feasible, but is not cost-effective from an operational economy standpoint. Another technically viable process which, however, needs further development and presented in this investigation, is the hydrometallurgical processing that involves acid leaching under oxygen pressure of ground ash, followed by electrolytic separation of nickel from sulphate solution and vanadium is then neutralized and precipitated by adjustment the pH value and calcined to produce V2O5.     

Development of a MSW classification system for the evaluation of mechanical properties

To date, sparse information is available on the mechanical properties of municipal solid waste and the results of published work are often hard to compare due to differences in waste composition and therefore properties. To allow comparison, a unified classification system for waste is deemed crucial. Existing classification systems are presented and discussed. For a geotechnical classification, mechanical properties, size, shape and degradability potential of waste components have to be taken into account. A new and improved classification system for waste components is proposed, which complies with the requirements of a geotechnical classification system. It classifies waste components based on: (1) their material engineering properties (e.g., shear, compressive and tensile strength), (2) a size distribution of the components, (3) the component shape (reinforcing, compressible and incompressible), and (4) the degree of degradability. The proposed classification system is applied to data from the literature and methods for presenting classification information are demonstrated. Further work required to develop a full classification system for waste bodies is highlighted.     

Screening tests for hazard classification of complex waste materials – Selection of methods

In this study we describe the development of an alternative methodology for hazard characterization of waste materials. Such an alternative methodology for hazard assessment of complex waste materials is urgently needed, because the lack of a validated instrument leads to arbitrary hazard classification of such complex waste materials. False classification can lead to human and environmental health risks and also has important financial consequences for the waste owner. The Hazardous Waste Directive (HWD) describes the methodology for hazard classification of waste materials. For mirror entries the HWD classification is based upon the hazardous properties (H1–15) of the waste which can be assessed from the hazardous properties of individual identified waste compounds or – if not all compounds are identified – from test results of hazard assessment tests performed on the waste material itself. For the latter the HWD recommends toxicity tests that were initially designed for risk assessment of chemicals in consumer products (pharmaceuticals, cosmetics, biocides, food, etc.). These tests (often using mammals) are not designed nor suitable for the hazard characterization of waste materials. With the present study we want to contribute to the development of an alternative and transparent test strategy for hazard assessment of complex wastes that is in line with the HWD principles for waste classification. It is necessary to cope with this important shortcoming in hazardous waste classification and to demonstrate that alternative methods are available that can be used for hazard assessment of waste materials. Next, by describing the pros and cons of the available methods, and by identifying the needs for additional or further development of test methods, we hope to stimulate research efforts and development in this direction. In this paper we describe promising techniques and argument on the test selection for the pilot study that we have performed on different types of waste materials. Test results are presented in a second paper.As the application of many of the proposed test methods is new in the field of waste management, the principles of the tests are described. The selected tests tackle important hazardous properties but refinement of the test battery is needed to fulfil the a priori conditions.     

Biodegradability of a Selected Range of Polymers and Polymer Blends and Standard Methods for Assessment of Biodegradation

Synthetic polymers are important to the packaging industry but their use raises aesthetic and environmental concerns, particularly with regard to solid waste accumulation problems and the threat to wildlife. Some concerns are addressed by attention to problems associated with source reduction, incineration, recycling and landfill. Others are addressed by the development of new biodegradable polymers either alone or in blends. Materials used for biodegradable polymers include various forms of starch and products derived from it, biopolyesters and some synthetic polymers. Starch is rapidly metabolised and is an excellent base material for polymer blends or for infill of more environmentally inert polymers where it is metabolised to leave less residual polymer on biodegradation. This should help to improve the environmental impact of waste disposal. A number of standard methods have been developed to estimate the extent of biodegradability of polymers under various conditions and with a variety of organisms. They tend to be used mainly in the countries where they were developed but there is much overlap between the standards of different countries and wide scope for development of consistent and international standards.     

Geotechnical quality assurance of construction of disposal facilities

This paper summarizes the technical resource document of the same name (U.S. EPA-600/S2-84-040, March 1984). Although the technical resource document is specifically addressed to the construction of hazardous waste disposal facilities within the U.S.A., most of the topics discussed and most of the general suggestions made are of universal applicability. The need for a quality assurance programme as a management practice which assures the protection of the human health and environment is discussed within the framework of the EPA regulations promulgated on 26 July 1982. The permittee of a hazardous waste disposal facility is shown to be somewhat unique in the construction industry given the three responsibilities, design, construction and operations, and quality assurance, all consolidated with him. The geotechnical parameters which should be tested, observed and documented during the construction, operation and closure of a disposal facility are identified. The limitations of design properties tests and the applicability of index properties tests are discussed. A summarized statistical analysis of sampling size, frequency and distribution to support a hazardous waste disposal facility quality assurance programme is presented. Accepted and commonly used methods for testing water content, unit weight, specific gravity, grain-size distribution, liquid limit, plastic limit, cohesive soil consistency, water content/density/compactive effort, cohesionless soil relative density, and geomembranes/geotextiles are identified. The criteria for the selection of a particular test method are discussed. A quality assurance programme, suitable for the somewhat unique permittee of a hazardous waste disposal facility, is presented. Considerations for such a quality assurance programme are also addressed.     

聚结晶紫膜修饰电极的制备及对水中对苯二酚和邻苯二酚的测定

通过电化学的方法将结晶紫聚合在玻碳电极表面制备聚结晶紫(PCV)膜修饰电极,并研究了对苯二酚和邻苯二酚在PCV膜修饰电极上的电化学行为。PCV膜修饰电极对对苯二酚和邻苯二酚的氧化有良好的电催化作用。在最佳的实验条件下,氧化峰电流在对苯二酚和邻苯二酚的浓度为4.0×10-6~2.8×10-4mol/L之间呈良好线性关系,对苯二酚和邻苯二酚的线性相关系数分别为0.9991和0.9823,检出限分别为6.2×10-7mol/L和9.0×10-7mol/L。PCV膜修饰电极具有良好的灵敏度、重现性和稳定性,可以应用于实际水样中两种物质的同时测定。     

Experimental determination of optimum gutter brush parameters and road sweeping criteria for different types of waste

The removal ability of gutter brushes for road sweeping for various debris types and different sweeping parameters is studied through experimental tests. The brushing test rig used comprises two commercial gutter brushes, a concrete test bed, and an asphalt test road with a gutter of 0.25 cm width and 10° slope. The brush-surface contact area is determined by sweeping sand on the concrete test bed. Sweeping problems are identified and discussed, and sweeping criteria for the different debris types are suggested. Also, optimum sweeping parameters are proposed for each debris type. In addition, debris removal mechanisms are discussed and analysed. The results indicate that for large heavy debris such as stones and gravel, it is not difficult to achieve large removal forces, because the steel bristles are relatively stiff. Conversely, high removal forces are not needed for particles of millimetre or micron sizes, but bristle curvature has to be appropriate to remove particles from road concavities. Finally, it is found that mud, especially dry mud on a rough surface, is the hardest debris to sweep, requiring a brush with a large tilt angle and a very large penetration to produce large removal forces.     

Hazard property classification of waste according to the recent propositions of the EC using different methods

Hazard classification of waste is a necessity, but the hazard properties (named “H” and soon “HP”) are still not all defined in a practical and operational manner at EU level. Following discussion of subsequent draft proposals from the Commission there is still no final decision. Methods to implement the proposals have recently been proposed: tests methods for physical risks, test batteries for aquatic and terrestrial ecotoxicity, an analytical package for exhaustive determination of organic substances and mineral elements, surrogate methods for the speciation of mineral elements in mineral substances in waste, and calculation methods for human toxicity and ecotoxicity with M factors.In this paper the different proposed methods have been applied to a large assortment of solid and liquid wastes (>1 0 0).Data for 45 wastes – documented with extensive chemical analysis and flammability test – were assessed in terms of the different HP criteria and results were compared to LoW for lack of an independent classification. For most waste streams the classification matches with the designation provided in the LoW. This indicates that the criteria used by LoW are similar to the HP limit values.This data set showed HP 14 ‘Ecotoxic chronic’ is the most discriminating HP. All wastes classified as acute ecotoxic are also chronic ecotoxic and the assessment of acute ecotoxicity separately is therefore not needed. The high number of HP 14 classified wastes is due to the very low limit values when stringent M factors are applied to total concentrations (worst case method). With M factor set to 1 the classification method is not sufficiently discriminating between hazardous and non-hazardous materials. The second most frequent hazard is HP 7 ‘Carcinogenic’. The third most frequent hazard is HP 10 ‘Toxic for reproduction’ and the fourth most frequent hazard is HP 4 “Irritant – skin irritation and eye damage”. In a stepwise approach, it seems relevant to assess HP 14 first, then, if the waste is not classified as hazardous, to assess subsequently HP 7, HP 10 and HP 4, and then if still not classified as hazardous, to assess the remaining properties.The elements triggering the HP 14 classification in order of importance are Zn, Cu, Pb, Cr, Cd and Hg. Progress in the speciation of Zn and Cu is essential for HP 14. Organics were quantified by the proposed method (AFNOR XP X30-489) and need no speciation. Organics can contribute significantly to intrinsic toxicity in many waste materials, but they are only of minor importance for the assessment of HP 14 as the metal concentrations are the main HP 14 classifiers. Organic compounds are however responsible for other toxicological characteristics (hormone disturbance, genotoxicity, reprotoxicity…) and shall be taken into account when the waste is not HP 14 classified.     

The effect of moisture on air classification of municipal solid waste

The effect of moisture on the air classification of municipal solid waste (MSW) is analysed using a 2³ factorial design. A synthetic MSW is used in the laboratory to facilitate controlled variation of composition and moisture content. A pilot scale 120 ° zig-zag air classifier is used to perform the classification tests. Ten system response variables are evaluated including six recoveries, two purities and two efficiencies, to elucidate the impacts of (1) increased particle density resulting from moisture absorption and (2) particle adhesion. Results indicate a significant decrease in paper recovery and efficiency with increasing moisture. However, no significant reduction in aluminum and iron recovery is observed. This suggests that adhesion of these particles to extracted combustible materials is not a significant factor in reducing extract purity. Instead, extract purity reduction is a result of paper recovery losses from increasing particle density. The degree of moisture effect for varied MSW composition is greater for feeds with lower fractions of adsorbent materials. A redefination of percent moisture based on the MSW absorbent fraction is suggested in order to account for this varied impact. The new definition, moisture absorbancy ratio, is the weight of the moisture in the MSW divided by the dry weight of the absorbent materials in the MSW.     

Uncertainty in Estimation of Wet Deposition of Sulphur

A model is described for predicting wet deposition ofsulphur in Britain from rainfall and site measurementsof ion concentration in precipitation. This modelincludes orographic enhancement of both rainfall andion concentration. The model output is comparedagainst available measurement data. Sensitivity anduncertainty analyses are used to predict the outputuncertainty. If the stated assumptions can be shown tobe correct, the wet deposition for Britain at the 5 kmscale is accurate to ±35% across the country. Theanalyses show a larger uncertainty in central Englandand a possible bias towards underestimation of wetdeposition, the latter being of importance incalculating critical load exceedances in remote areas.     

空气涡轮制冷低温粉碎法回收废弃橡胶

利用带回冷循环的空气涡轮制冷系统，在低温条件下，将废旧橡胶进行冷冻、粉碎、制成６０目以上的精细胶粉。此法的冷冻能耗成本仅为国际上通用的液氮法的１／１０，整具工艺过程不产生二次污染，为废旧橡胶的综合利用提供了一条新途径。     

Factors and values of willingness to pay for improved construction waste management--a perspective of Malaysian contractors

Malaysia is facing an increase in the generation of waste and of accompanying problems with the disposal of this waste. In the last two decades, extensive building and infrastructure development projects have led to an increase in the generation of construction waste material. The construction industry has a substantial impact on the environment, and its environmental effects are in direct relation to the quality and quantity of the waste it generates. This paper discusses general characteristics of the construction contractors, the contractors' willingness to pay (WTP) for improved construction waste management, determining factors which affect the amount of their willingness to pay, and suggestions and policy implications in the perspective of construction waste management in Malaysia. The data in this study is based on contractors registered with the construction industry development board (CIDB) of Malaysia. Employing the open ended contingent valuation method, the study assessed the contractors' average maximum WTP for improved construction waste management to be RM69.88 (1US$=3.6 RM) per tonne of waste. The result shows that the average maximum WTP is higher for large contractors than for medium and small contractors. The highest average maximum WTP value is RM88.00 for Group A (large contractors) RM78.25 for Group B (medium-size contractors) and RM55.80 for Group C (small contractors). One of the contributions of this study is to highlight the difference of CIDB registration grade in the WTP for improved construction waste management. It is found that contractors' WTP for improved waste collection and disposal services increases with the increase in contractors' current paid up capital. The identified factors and determinants of the WTP will assist the formulation of appropriate policies in addressing the construction waste problem in Malaysia and indirectly improve the quality of construction in the country.     

Report: examples of capacity building cooperation.

Odense Waste Management Company Ltd. (OWMC) covers the municipality of Odense having around 185 000 inhabitants. It is a not-for-profit company, in which all services are paid for by the users. OWMC is increasingly participating in international development activities, particularly within training and operational support. This is mainly driven by the staff, who think it is important, interesting, challenging and fun to contribute their know-how elsewhere. The main approach applied, when training and practice is undertaken for OWMC's own staff as well as for international cooperation partners, is to keep things simple and easily understandable, even if there may sometimes be rather complex processes and activities involved. So far, OWMC has in 2003-2005 participated in a project for the municipalities of Koszalin and Slupsk in Northern Poland, and in 2005-2007 in a project for the newly established solid waste management departments of Beni Suef and El Fashn cities in Egypt. Would it be possible to create a future waste management sector with more know-how sharing mechanisms in place, and might the establishment of a capacity building working group or networking forum, for example, within the framework of ISWA be an important step forward in this context? Why not just start now?