Environmental policy with collective waste disposal

Centralized collection and disposal is an integral component of waste management strategies for many solid and liquid wastes, and carbon capture and storage is currently being considered for gaseous waste. In this paper we show how collective waste disposal systems introduce essential changes in the design of optimal environmental policy. Absent collective disposal, an optimal environmental policy imposes relatively stringent regulations on polluters in regions where local environmental damage functions are “high”; however, under collective waste disposal, the optimal environmental policy level increases monotonically over distance from the disposal site, and this is true irrespective of the degree of spatial heterogeneity in local environmental damage functions. We characterize the optimal spatial pattern of environmental policy levels under collective waste disposal and identify optimal membership size for waste disposal networks comprised of homogeneous producers.     

Abfallwirtschaftskonzept im Rahmen eines Integrierten Umweltmanagementsystems

Economic regulations on recycling and respective waste disposal legislation will increasingly demand the realization of new waste management concepts. They do not stem from a ministerial goal in itself, but instead offen the enterprizes a chance to develop their own waste disposal strategies with a goal toward the future. In the course of an Intra-company analysis, this waste disposal concept must take the operative organization, the relevant processes and manufacturing techniques, the accumulation of waste in the cost centers as well as the waste disposal and utilization into consideration. Fundamental principles include the environmental regulations applicable to the enterprize in the form of both federal decress and injunctions. An environmental examination report demonstrates the methodical possiblities for stock-taking and makes it possible to identify the measures necessary for improving the operational waste disposal situation. The mandatory data acquisition and a feasible waste monitoring network can be used in the course of environmental management system for making an expert opinion by an independent, reputable environmental verifier.     

Ecofriendly approach of urban solid waste management: a case study of Jalgaon city, Maharashtra

In India, the traditional methods are used for urban solid waste management. These practices are associated with degradation of the urban environment Hence, an environmentally sound garbage management system is required for the urban waste management. The concept of waste minimization needs to be adopted in such systems. It is possible to implement certain corrective measures at collection, storage, transport and disposal of urban solid waste to minimize the adverse impacts on the environment The present investigations are emphasized on generation, characterzation and ecofriendly disposal of solid waste generated in Jalgaon city, Maharashtra. In the present study the waste generation at source was studied in the various income groups of the city. The per capita waste generation was studied by sampling the waste directly from the source of generation. The study reveals that the waste generation is large in the high-income group followed by middle and low-income group public. Further the physicochemical characterization of the waste was also studied. The data generated will help to develop environmentally sound and economically feasible solid waste management system for Ihe city.     

城市生活垃圾处置过程中环境污染防治

对我国城市生活垃圾处置技术发展现状进行了综述，着重阐述了垃圾处置过程中存在的废塑料、废电池、焚烧炉烟气等二次污染问题，指出应高度重视垃圾处置过程中环境污染防治问题。     

Economic Efficiency Effects of Alternative Policies for Reducing Waste Disposal

Reducing the amount of municipal solid waste that is disposed of has become an important policy goal. Previous research argued that a virgin material tax offered an efficient method of meeting this goal and it continues to be considered as a policy option today. This paper demonstrates, however, that a virgin material tax is not an efficient method of reducing waste, but that an alternative policy-a combined disposal tax and reuse subsidy-is. The combined disposal tax and reuse subsidy is theoretically consistent with unit-based household charges for waste disposal, but may have advantages in some situations.     

Gypsum Waste Disposal: Land vs Sea or Recycling

The disposal of waste gypsum wallboard at landfill sites in British Columbia (B.C.), Canada, resulted in the generation of hydrogen sulphide gas and toxic leachates. Although some remedial measures were taken to reduce or eliminate problems resulting from past dumping practices, many landfill operators refused to accept new waste for fear of litigation over the pollution of nearby streams and rivers. with the availability of legitimate disposal sites greatly reduced, a serious waste management problem arose. the two most promising options for reducing the accumulating waste appeared to be recycling and ocean disposal.

Agricultural use of the waste for soil conditioning would account for only a small portion of the waste generated annually. Manufacturing plants were reluctant to accept waste gypsum with a high paper fibre content for fear it would lower the quality of the new wallboard product or interfere with the existing equipment and processes in the plants. the technology for economically removing and separating the paper from the used or substandard wallboard had yet to be developed.

The environmental implications of disposal at sea were assessed by a government advisory committee under the provisions of the Canadian Environmental Protection Act. Although results of a test dump in internal waters of B.C. were positive, the committee felt that valuable amenities of nearshore waters would only be assured by restricting dumping to a remote offshore location. an acceptable disposal method with minimal impact on the marine environment was eventually found with appropriate pretreatment of the waste and the use of remotely controlled bottom dump scows. Recent progress in the processing of waste wallboard to make it acceptable to the manufacturing industry should significantly reduce if not eliminate the need to dispose of gypsum wallboard wastes at sea.     

德国的污泥利用和处置（Ⅰ）

文章论述了德国的污泥利用和处置情况,首先概述了德国的废物立法及其发展。然后比较了欧共体和德国污泥农用法规中的基本要点。随着分析了过去几十年德国的污泥产星的发展和组成,这和比较了德国汛泥和利用和处置的工艺。     

Estimation of municipal solid waste generation and landfill area in Asian developing countries

In developing Asian countries, the municipal cooperations are unable to handle the increasing amount of municipal solid waste, which into the uncollected waste being spread on roads and in other public areas leading to tremendous pollution and destruction of land and negative impact on human health. Generation of municipal solid waste increases with the rapid urbanization and accelerated economic development with in the rapidly growing advanced technological societies. The nature of municipal solid waste is a term usually applied to a heterogeneous collection group of waste produced in urban areas, the nature of which varies from region to region. The common problem faced by all developing Asian countries, is the disposal of municipal solid waste and availability of land fill site area. Present study explains the correlation analysis of among different factors of municipal solid waste and the objective is to assess the future municipal solid waste stream in Asian developing countries. The other goal of this study was to calculate the future land area that would be required for landfill site disposal in Asian developing countries.     

Hazardous waste management in educational and research centers: a case study

The hazardous waste management (HWM) practice at Tehran University of Medical Sciences Central Campus, Iran, was investigated in this study. Four schools were selected and the required information such as type and amount of wastes, temporary storage methods, waste discharge frequency, and final waste disposal methods using sampling, questionnaires, interviews with laboratory staff, and reference to available documents were gathered. The quantity of hazardous waste generation per year excluding the uncontrolled wastewater was found to be 2.072 tons per year. The obtained results show that wastes having features of being infectious, toxic, ignitable, carcinogenic, corrosive, and reactive were present at 32%, 28%, 16%, 14%, 8%, and 2%, respectively. In the central campus, hazardous solid wastes managed with household solid wastes and hazardous liquid waste were discharged into the sinks without any kind of control; improper HWM practices are evident from the point of waste production to final disposal.     

中国废电池管理对策分析

针对废电池管理体系中存在的管理法规不完善,回收体系不健全,适宜的管理运行机制等问题,探讨了如何加强废电池环境无割化管理的方法,提出加强管理法规建设、完善废电池自愿、强制回收体系、     

Medikamentenentsorgung in privaten Haushalten: Ein Faktor bei der Gewässerbelastung mit Arzneimittelwirkstoffen?

Background

Residues of pharmaceuticals are meanwhile detected widely in the aquatic environment. Waste water treatment plants are the main route of entry: after intake the agents or their metabolites are excreted predominantly via urine into the sewage. Largely unknown is, however, if the improper disposal of unused medicines via domestic sanitary devices (toilet or sink) contributes to the measured concentrations in the environment. Aim of this investigation was to clarify to what extent consumers in Germany dispose of unused medicines directly via domestic sewage. In July and August 2006 a representative survey of the population with 2.000 interviewees was performed for this purpose.

Results

The analysis of the survey shows that the disposal of unused medicines via domestic sewage takes place on relevant scales: approx. 16% of the population dispose at least occasionally of unused or expired tablets in the toilet whereas 43% proceed alike with liquid drugs (toilet or sink).

Discussion

A possible reason for this disposal behaviour is the widely inconsistent waste disposal communication by the municipalities and the federal states. The resulting uncertainty about the correct way to dispose of unused medicines gains in importance in the context of the high recycling willingness of the (German) population: appropriate disposal options for drug residues (tablets or liquids) arising from waste separation are often not realised.

Conclusions

Quantitative assessments on the basis of the collected data demonstrate that the established frequency of direct disposal of unused medicines via domestic sewage can partly contribute significantly to the occurrence of pharmaceuticals in the aquatic environment. Crucial parameters are here the excretion rate of the active pharmaceutical ingredient considered and the actual amount of medication waste.

Recommendations

Based on the inquiry results, measures that lead to a more adequate handling of pharmaceutical waste disposal are demanded. The establishment of a consistent and binding disposal standard for unused medicines via return in pharmacies is recommended. This measure needs to be accompanied by a simplification of the established take back systems which partly cause high time and effort for pharmacies.     

Ökonomisch-organisatorische Betrachtung der Klärschlammverwertung: Kosten — Nutzen — Ausstiegsszenarien

Goal and Scope

The controversial issue of disposing municipal sewage sludge on arable farmland and growing demand on derived fuels could result in a total or partial abandoning of sludge recycling as fertiliser. Alternative disposal strategies like incineration will cause complex changes. A material flow management framework is used to determine the economic-organisational consequences for public authorities, farmers, rural contractors, disposal firms, and population in Schleswig-Holstein.

Methods and Focus

The study is based upon network analysis, analysis of agricultural and wastewater statistics and interviews. After structuring the disposal process, transaction are used to derive costs of different disposal strategies. The purification technique of sewage plant and application of metal salts for precipitation affect the fertilising quality of sludge. Therefore, all plants are classified into 4 different technical groups with decreasing fertilising effect. Now, the amount of sludge and corresponding fertilising benefit is calculated both state wide and for typical farms. Finally costs of different disposal strategies are derived.

Results

Referring to sewage plants sludge disposal in Schleswig-Holstein is characterised by a local structure since less than 10% of all 841 sewage plants produce almost the entire sludge where as many small plants especially in rural areas produce only little amounts. Usually enriched with lime, dewatered sludge fulfilling legal limits is used as organic fertilizer. The number of transactions indicates the costs.

Discussion

To reduce transaction costs, disposal firms try to offer high quantities of sludge to a limited number of farmers. Due to purification technique, the fertilising effect of half the amount of total sludge is reduced. Compared to the total demand on phosphorous, sludge can only substitute up to 4% of phosphorous. Farmers can substitute up to 50% of mineral fertiliser and increase marginal income per hektare. Although changing disposal strategy to incineration would double economic costs, fee for wastewater would remain almost constant.

Conclusions

Small wastewater plants, farmers and rural contractors would be particularly affected by ceasing sludge disposal. Small wastewater plants would have to invest in dewatering equipment, rural contractors would lose an important market segment and farmers (only a small percentage of all farmers uses sludge) would lose additional income. Changing waste management from sludge disposal with many involved parties to e.g. incineration would considerably reduce transaction costs for authorities. In case of partly changing waste management strategy, whereas sludge of small plants could be recycled, the authorities would still have to plan and control the disposal process even for small quantities of sludge. Transaction costs do not decrease proportionally to the decreasing amount of sewage sludge.

Perspectives

Quality management systems initiated by disposal firms should increase the acceptance and prevent a ban of sludge recycling. Nevertheless, the waste market develops from material to energetic use of waste. Significant resources will be lost without a phosphorous recovering from sludge as well as from other organic waste.     

废旧电池资源化、无害化

对当前国内外在废旧电池的处理处置方面进行了综合性论述,对废旧电池的危害及当前应采取的对策进行分析。     

Municipal solid waste,an overlooked route of transmission for the severe acute respiratory syndrome coronavirus 2: a review

Environmental Chemistry Letters - Municipal solid waste could potentially transmit human pathogens during the collection, transport, handling, and disposal of waste. Workers and residents living in...     

Biochar from municipal solid waste for resource recovery and pollution remediation

Environmental Chemistry Letters - Open dumping of municipal solid waste is a common method of waste disposal in developing countries, thus leading to pollution by gaseous emissions and landfill...     

城市生活垃圾治理过程的能源化技术

论述了垃圾多种治理技术以及这些技术中的能源化的关键。这些技术涉及垃圾卫生填埋、垃圾梦烧、垃圾衍生燃料技术、垃圾厌氧发酵和垃圾的热解气化等。针对中国垃圾的具体特点，对中国垃圾能源化提出一些初步方案和建议。     

The problem of arsenic disposal in non-ferrous metals production

Arsenic is a minor and inevitable component of all inputs to the non-ferrous metals extraction industry but sales are only a small proportion of input. Safe disposal of the excess is a substantial problem. Public perception exaggerates the toxicity of arsenic and generates emotional reactions, whereas arsenic has a natural cycle in the environment and all life is tolerant to traces with detoxication processes to deal with excess. Toxicity data for overload doses to biota in general are poor when required for the formulation of standards for disposal of waste thus making difficult the legal definition of hazardous wastes for appropriate regulation. Suitable tests to determine the stability of a waste for safe disposal are complex, costly, and uncertain against the need for the waste to be in place for a very long time. Further, there is no universal agreement on the principles which should govern the means of disposal of hazardous wastes. Safe disposal of arsenical wastes is thus difficult but practical and convincing solutions must still be devised, guided by thermodynamics and by natural processes. Much judgement and goodwill are required. However, few if any arsenical substances are so stable to moist air that they will not release unacceptable concentrations of arsenic when left in a thermodynamically open dump. Control of hot spot dumps must therefore start with planning of location and configuration, and the wastes must be sealed to exclude air and water and to contain leachates indefinitely. This is very difficult to ensure. Registration, control and testing of waste stability and dump behaviour must be planned on the assumption that leakage will arise at some time in future millennia, a major and expensive logistical problem. Adsorption of arsenate by soils and aquatic sediments is an important buffering and fixing process for any leakage, but waters can still be polluted. It is, however, argued that deliberate retention of leachate can lead to problems from uncontrolled future leakages, and thus that "hot spot dumps should be designed to allow controlled leakage within the capacity of the receiving environment. Better still would be efficient dilution and dispersal. Marine disposal may be politically unattractive, but the arsenic reports to sediments and the process copies nature. It is probably the best environmental disposal option where practicable.     

Ablagerung toxischer Chemieabfälle im August 2006 in Abidjan, Republik Côte d’Ivoire: Versuch einer Rekonstruktion

Background

Globally, every year several hundred million tons of problematic, e.g. chemical, wastes are generated stemming to more than 90% from the 25 OECD countries. Due to their partly considerable toxicity special and often expensive measures are required for their disposal. According to the Secretary of the ‘Basel Convention on the Control of Transboundary Movements of Hazardous Waste and Their Disposal’ annually at least 8.5 million tons of wastes are transboundarily traded. Although the ‘Basel Convention’ has set up rules how to handle international waste streams, certain waste amounts are illegally transported from the OECD countries to developing countries — basically for reasons of expenses. Often an environmental safe treatment of toxic waste is not ensured or even not possible in the receiving countries. As set forth in a report of the European Network for the Implementation and Enforcement of Environmental Law (IMPEL) published in 2006, the illegal trade with toxic waste has steadily increased. 3000 shipping documents of 17 European seaports were examined and 258 cargo holds were inspected showing that 68 of 140 waste shippings were illegal. Preventing illegal transports of waste meets with various obstacles. Controlling measures require considerable personal, technical, and logistic resources that are not sufficiently available in each country concerned. Missing or ineffective administrative structures hamper fast actions to stop illegal waste disposal. Partly, the political will to take the necessary steps is lacking. An additional problem is the fact that waste that is obtained from the regular shipping business is not subject to the Basel Convention but to the ‘International Convention for the Prevention of Pollution from Ships’. The implementing statures are summarized in the document MARPOL 73/78; the International Maritime Organization (IMO) is responsible. Identifying the origin of waste and thus defining the responsibility occasionally raises difficulties. This background provides a basis to try to reconstruct the course of events concerning the disposal of chemical waste in Abidjan.

Methods

Several information sources were utilized to reconstruct the course of events at Abidjan in August 2006; e.g. public press, declarations of international governmental organizations, especially of the UN and of its subsidiary organizations, communiqués of the Secretary of the Basel Convention, and statements of several NGOs. Nevertheless a complete reconstruction of the incident is impossible, since a detailed and reliable historical report is not available. Furthermore the responsible politicians have not undertaken significant efforts to shed light upon the incident. Additionally relevant documents of the participating companies are not available to the public.

Conclusions

The analyzed incident makes obvious that the control mechanisms of the Basel Convention can be circumvented. It remains unclear who has to take the political responsibility for the death of 10 people and for the health defects of thousands of humans. Possible civil and criminal consequences are not foreseeable for the actors and company owners involved in the illegal waste dumping. The people of Abidijan are confronted with unresolved questions regarding the occurrence of chronic diseases and possible long-term effects of remaining waste portions.

Recommendations and Perspectives

The incident demonstrates that the control of the transboundary transport and disposal of hazardous waste needs to be enforced and legal grey areas should be eliminated. It should be a task of the OECD countries and of all other economically and technically developed countries and organizations to support the developing countries’ efforts to build up the personal, technical, and infrastructural capacities for an efficient control of waste imports.     

Policy options for toxics disposal: Laissez-faire,subsidization, and enforcement

This paper evaluates three second-best policies for dealing with the problem of illegal hazardous-waste disposal. The first is a laissez-faire policy; the second is a policy under which legal disposal of hazardous waste is subsidized; the third is a policy that discourages illegal disposal by increasing the expected penalty associated with illegal disposal. Using a simple computational model, I compute the optimum subsidy and the optimum enforcement budget, and determine the conditions under which each policy option is superior to others.