总结经验,进一步推进全国循环经济发展

作者全面阐述了当前我国发展循环经济的重要性、存在的问题,并提出了下一步工作的意见。     

论知识经济下经济安全评估及策略

随着知识经济的来临,经济全球化趋势越来越明显,国家间的经济联系不断增强,同时也随之产生的国家间的经济竞争不断加剧,使得国家经济安全受到威胁。笔者针对当前的经济发展特征,就如何提高国家经济安全水平以增强国际竞争力探讨了影响国家经济安全的因素。从多方面的、综合性的影响经济安全因素中,找到影响经济安全的基本要素,据此从统计的可行性角度,科学地构建了评估经济安全的指标体系。所构建的指标体系对综合评价一个国家和地区的经济安全具有一定的合理性和科学性。最后,提出了有关保证经济安全的策略,以便当我国在知识经济来临之时,保证经济快速发展,能在经济全球化中不断提高自己的国际竞争力。     

县域经济所有制结构的调整

县域经济的所有制结构所表现出来的经济实体形式包括县属地方国有经济、多种形式的集体经济和民营经济,探讨了县域经济所有制结构的形式及其在市场经济中的作用.     

欠发达地区县域经济可持续发展障碍与对策--以云南省凤庆县为例

通过对区位优势不明显,社会、经济和文化落后,但资源丰富的典型的欠发达县域凤庆县的实证研究,从思想观念、所有制结构、产业结构、基础建设、社会文化和经济,以及生态环境和农业基础等方面剖析了凤庆县经济不可持续发展的主要症结及原因,提出了该县经济可持续发展的总体思路,并作了对策探讨.     

实施循环经济推动大型煤炭企业可持续发展

经济发展与环境保护之间的矛盾,一直是困扰国有大型煤炭企业发展的大问题,循环经济模式能够从根本上解决这一矛盾.本文以龙口矿业集团公司为例,论述了发展循环经济是实现煤炭企业可持续展的必由之路.     

大力发展循环经济促进宁阳县可持续发展

宁阳县发展循环经济过程中所取得的初步成果,同时对当前存在的突出问题,提出了相应的对策和改进措施:制定促进循环经济发展的相关政策;构筑循环经济基本模式,推动建立生态工业园;建立循环经济发展的技术支撑体系;制定发展循环经济的长远规划;提高全民发展循环经济意识和公众参与水平.     

企业逆向物流与循环经济立法之联系

逆向物流给企业带来效益的同时,也带来了生态物流的理念.逆向物流涉及了经济与生态环境两大系统,显现出了自身的特点与积极因素.逆向物流充分体现了循环经济发展之宗旨.加速循环经济的立法,并以相应立法来推动企业尽快实施物流活动是至关重要的.     

SUMMER LOW FLOWS IN NEW ENGLAND DURING THE 20TH CENTURY1

ABSTRACT: High springtime river flows came earlier by one to two weeks in large parts of northern New England during the 20th Century. In this study it was hypothesized that late spring/early summer recessional flows and late summer/early fall low flows could also be occurring earlier. This could result in a longer period of low flow recession and a decrease in the magnitude of low flows. To test this hypothesis, variations over time in the magnitude and timing of low flows were analyzed. To help understand the relation between low flows and climatic variables in New England, low flows were correlated with air temperatures and precipitation. Analysis of data from 23 rural, unregulated rivers across New England indicated little evidence of consistent changes in the timing or magnitude of late summer/early fall low flows during the 20th Century. The interannual variability in the timing and magnitude of the low flows in northern New England was explained much more by the interannual variability in precipitation than by the interannual variability of air temperatures. The highest correlation between the magnitude of the low flows and air temperatures was with May through November temperatures (r =?0.37, p= 0.0017), while the highest correlation with precipitation was with July through August precipitation (r = 0.67, p > 0.0001).     

Using long-term data for a reintroduced population to empirically estimate future consequences of inbreeding

Inbreeding depression is an important long-term threat to reintroduced populations. However, the strength of inbreeding depression is difficult to estimate in wild populations because pedigree data are inevitably incomplete and because good data are needed on survival and reproduction. Predicting future population consequences is especially difficult because this also requires projecting future inbreeding levels and their impacts on long-term population dynamics, which are subject to many uncertainties. We illustrate how such projections can be derived through Bayesian state-space modeling methods based on a 26-year data set for North Island Robins (Petroica longipes) reintroduced to Tiritiri Matangi Island in 1992. We used pedigree data to model increases in the average inbreeding level (F ) over time based on kinship of possible breeding pairs and to estimate empirically N_e/N (effective/census population size). We used multiple imputation to model the unknown components of inbreeding coefficients, which allowed us to estimate effects of inbreeding on survival for all 1458 birds in the data set while modeling density dependence and environmental stochasticity. This modeling indicated that inbreeding reduced juvenile survival (1.83 lethal equivalents [SE 0.81]) and may have reduced subsequent adult survival (0.44 lethal equivalents [0.81]) but had no apparent effect on numbers of fledglings produced. Average inbreeding level increased to 0.10 (SE 0.001) as the population grew from 33 (0.3) to 160 (6) individuals over the 25 years, giving a ratio of 0.56 (0.01). Based on a model that also incorporated habitat regeneration, the population was projected to reach a maximum of 331–1144 birds (median 726) in 2130, then to begin a slow decline. Without inbreeding, the population would be expected stabilize at 887–1465 birds (median 1131). Such analysis, therefore, makes it possible to empirically derive the information needed for rational decisions about inbreeding management while accounting for multiple sources of uncertainty.     

Landfill reduction experience in The Netherlands

Modern waste legislation aims at resource efficiency and landfill reduction. This paper analyses more than 20 years of landfill reduction in the Netherlands. The combination of landfill regulations, landfill tax and landfill bans resulted in the desired landfill reduction, but also had negative effects. A fierce competition developed over the remaining waste to be landfilled. In 2013 the Dutch landfill industry generated €40 million of annual revenue, had €58 million annual costs and therefore incurred an annual loss of €18 million. It is not an attractive option to prematurely end business. There is a risk that Dutch landfill operators will not be able to fulfil the financial obligations for closure and aftercare. Contrary to the polluter pays principle the burden may end up with society. EU regulations prohibiting export of waste for disposal are in place. Strong differentials in landfill tax rate between nations have nevertheless resulted in transboundary shipment of waste and in non-compliance with the self-sufficiency and proximity principles. During the transformation from a disposal society to a recycling society, it is important to carefully plan required capacity and to guide the reorganisation of the landfill sector. At some point, it is no longer profitable to provide landfill services. It may be necessary for public organisations or the state to take responsibility for the continued operation of a ‘safety net’ in waste management. Regulations have created a financial incentive to pass on the burden of monitoring and controlling the impact of waste to future generations. To prevent this, it is necessary to revise regulations on aftercare and create incentives to actively stabilise landfills.