A Comparative Overview Of Recycling In London And Hamburg

The level of recycling for household waste is significantly higher in Hamburg than in London, yet the extent of materials recovery in both cities is well below technically achievable levels. This paper shows that the higher level of recycling in Hamburg can be accounted for by three main factors: a higher density of recycling facilities combined with the use of more sophisticated collection systems such as a dual-bin service for putrescible wastes; a unified administrative structure for waste management under direct control of an elected regional government; and finally, a system of proportional representation in local government allowing environmentalist political demands to be directly translated into public policy. Despite these differences however, both cities face difficulties with the expansion of recycling derived from the weakness of the secondary materials market, the lack of legislative control over the size and composition of the waste stream, the fiscal constraints on local government and the expense of comprehensive recycling programmes in comparison with alternative forms of waste disposal. This paper concludes that the high cost of recycling presents a fundamental political dilemma for sustainable waste management policy in developed economies.     

Solid Waste Recycling And Reuse In Bangkok

Materials recovered from solid waste in Bangkok are mainly glass bottles, paper and paper products, plastic products and metals. Materials are separated at three different stages of the collection process: at the source, prior to collection; by the crews of the collection vehicle; and by the scavengers at the dump site. The total daily tonnage of recyclable garbage collected at the source by the waste pickers is estimated at 286 tonnes, about 5% of the garbage collected by the city. There are small scale recycling shops (SSR) located around the main disposal sites where collected materials are sold by the collection crews and the scavengers. The quantity of materials delivered to the SSR shops by the collection crew vary between 1-6 tonnes per day. The amount of materials recovered by the scavengers (at the dump site) varies between 50-150 kg person^-1 day^-1. Therefore around 7.5% of the solid waste is recycled. In Bangkok both formal and informal sectors manufacture paper pulp, cardboard boxes and magazines from the recyclable paper. Paper products which account for 55% of the total waste stream are considered as the largest "product group" in the municipal solid waste. Recyclable glass (1-3% of the total waste stream) or cullet is used to manufacture plain glasses or cups. Plastics constitute about 10-15% of the waste stream. The benefit/cost ratios of production of most of these industries were reported to be higher than 1.5. In order to enhance recycling, legislative measures need to be introduced and enforced. In Thailand, there is, however, no law concerning recycling. There is no incentive for the consumer to separate solid waste for recycling, as the prices of waste in Bangkok are low and inconsistent. Therefore the pricing system should be more organized for recycling to be more effective.     

The future course of solid waste management in the U.S.

It is postulated that the current “garbage crisis” is due to a shortage of disposal capacity, not to burgeoning amounts of municipal solid waste (MSW). In support of this, trends in the quantity and composition of MSW, methods of waste reduction, recycling and growth of waste-to-energy capacity are examined to gain insight as to the future course of MSW management in the U.S. over about the next 15 plus years. This is the likely time to install new disposal capacity if pending legislative proposals are passed, that would enable states that provide their own disposal to ban wastes from other states.A new term, the “intensity of waste generation”, is proposed and illustrated, analogous to the intensity of mineral usage. The intensity is decreasing, implying that it is unlikely that waste generation will grow at rates projected by extrapolation or simple macroeconomic assumptions. Some other conclusions are: per capita MSW generation was nearly statistically constant from 1970 to 1984; the content of most forms of packaging in MSW are decreasing; packaging decreases the amount of food residues in MSW; and proposed national recycling targets of about 25% or more are not likely to be achieved, in part because of changes in the composition of MSW. Coupled with likely shortages of labor to process separated waste, it is forecast that there will be some future time when people will not think source separation is worth the bother and recycling will decrease. The future growth of waste-to-energy capacity is projected by assuming that a city will install capacity when others have done so, which leads to a simple quantitative model. The likely effects of impending landfill and incineration regulations are addressed.     

Municipal sewage sludge use in forests of the pacific northwest,U.S.A.: Environmental concerns

Forest applications of dewatered municipal sludge in Washington State, U.S.A. were monitored for heavy metals, pathogens, and nitrates. Heavy metals did not leach from the sludge in significant quantities and remained associated with the sludge for at least four years. Tree seedlings grown in sludge-amended soil and compost accumulated moderate metal levels, but growth was not adversely affected. Populus seedlings took up more metal than coniferous seedlings. Some coniferous seedlings grown directly in unamended sludge had reduced growth and developed symptoms of nutrient imbalances. Fecal coliform and total coliform levels in sludge were initially high, but decreased to background levels in 1.0–1.5 years, suggesting that site access should be limited for a time after application. Bacterial movement in the soil was limited and very few viable bacteria reached the groundwater. Aerosols may be generated during sludge applications. Nitrogen leaching is a major environmental concern or sludge application. Heavy applications resulted in high NO₃⁻ levels in soils and groundwater. A significant fraction of the nitrogen loss was in gaseous form. Sludge applications in forests can be environmentally sound if application rates are matched to site characteristics.     

Residential solid waste generation and recycling in the U.S.A. and Japan

The generation rates of each residential solid waste component was determined for test areas in the U.S.A. and Japan. To keep the results consistent; single family dwelling areas in Madison (U.S.A.) and Sapporo (Japan), which have similar characteristics, were selected as test areas; the same survey methods were employed in both cities; all waste material from households, including recycled material, was estimated. The average person in Madison was found to produce twice the amount of paper waste, half the amount of food waste but approximately the same quantity of total residential waste (other than yard waste) as in Sapporo.     

Short-term/Long-term Solutions In Waste Management: Economics And The Transition Process

Cleaner technology and recycling, as the preferred solution to waste management, is increasing in implementation but not at the rate expected given the successes and paybacks associated with those strategies. The reasons for the delay in implementation lie in the conflict between short-term and long-term solutions. The factors that contribute to hindrance or facilitation of the transition are found in: a) the distinction between the short-term and the long-term at a technical level; b) the distinction between the short-term and the long-term at a political level; c) the investment decision at the firm level; and d) related investments in infrastructure, organization, and institutions. This article identifies which constraints will disappear with time, which constraints are institutional and will require deliberate modification, and which constraints are permanent and must be considered part of the costs of the long-term solution. The goal is not to argue against short-term solutions, but for the need to acknowledge unavoidable costs associated with the transition from the short-term to the long-term solution.     

Use of Natural 35S to Trace Sulphate Cycling in Small Lakes,Flattops Wilderness Area,Colorado, U.S.A.

Measurements of the cosmogenically-produced ³⁵S, a radioisotope of sulphur (t_1/2 = 87 days), are reported for the Ned Wilson Lake watershed in Colorado. The watershed contains two small lakes and a flowing spring presumed to be representative of local ground water. The watershed is located in the Flattops Wilderness Area and the waters in the system have low alkalinity, making them sensitive to increases in acid and sulphate deposition. Time series of ³⁵S measurements were made during the summers of 1995 and 1996 (July–September) at all three sites. The system is dominated by melting snow and an initial concentration of 16–20 mBq L^-1 was estimated for snowmelt based on a series of snow samples collected in the Rocky Mountains. The two lakes had large initial ³⁵S concentrations in July, indicating that a large fraction of the lake water and sulphate was introduced by meltwater from that year's snowpack. In 1995 and 1996, ³⁵S concentrations decreased more rapidly than could be accounted for by decay, indicating that other processes were affecting ³⁵S concentrations. The most likely explanation is that exchange with sediments or the biota was removing ³⁵S from the lake and replacing it with older sulphate devoid of ³⁵S. In September of 1995 and 1996, ³⁵S concentrations increased, suggesting that atmospheric deposition is important in the sulphate flux of these lakes in late summer. Sulphur-35 concentrations in the spring water were highly variable but never higher than 3.6 mBq L^-1 and averaged 2 mBq L^-1. Using a simple mixing model, it was estimated that 75% of the spring water was derived from precipitation of previous years.     

Lessons learned outfitting the U.S. Coast Guard with oil pollution equipment

Lessons learned procuring U.S.$30 500 000 of oil pollution recovery equipment for the United States Coast Guard (USCG) in response to requirements of the Oil Pollution Act of 1990 (OPA-90) are presented. A generic requirements analysis and a selection process useful for making equipment acquisitions and staging site selections are described. Response mission, oil spill threat, response area peculiarities, available resources, equipment capabilities, training requirements and life cycle costs are all factors which must be carefully considered in outfitting a response organization. A method to ensure you obtain quality equipment which meets your functional requirements is outlined. Long range concerns about logistics support, training and maintenance are also important considerations.Leveraging existing resources such as existing USCG vessels, commercial vessels available on short notice for lease and the original oil response equipment inventory of the two USCG Strike Teams proved to be extremely cost effective. Selection of a vessel of opportunity skimming system (VOSS) and outfitting replacement offshore buoy tenders with an on-board spilled oil recovery system (SORS) eliminated the costly option of procuring dedicated pollution response vessels which are generally underutilized as a single mission platform. A first article field and factory acceptance testing program ensured all equipment functioned as specified, eliminating costly errors. This process also provided valuable customer input and significant equipment improvements before production started. Quality assurance testing and Government oversight ensured production units were fabricated properly with specified materials identical to the approved first articles adding reliability to the entire delivered system. Staging equipment at three Strike Teams and 19 sites near existing Coast Guard buoy tenders best used the available personnel and vessel resources adjacent to primary oil spill threat areas.     

Pet Waste Management by Chemical Recycling: A Review

The paper reviews the problem due to the use and disposal of synthetic polymers to the environment and its solutions; in particular poly (ethylene terphthalate). Wide spread application and non-biodegradability of the PET creates huge amounts of waste and disposal, tend to a serious problem. The most important cause for recycling and reprocessing the waste PET has arisen from the awareness and concern for environmental pollution. To manage this various methods of polymer recycling has been proposed. Among them chemical recycling, i.e. hydrolysis, methanolysis, glycolysis and aminolysis are reviewed in detail. Appropriate technology and waste disposal procedures based on the socio-economic aspect to solve this problem are suggested.