中国铜产业体系演化的碳中和实现机制研究

本文研究了我国铜产业采选、冶炼、加工和再生等环节的演化趋势,构建了铜产业直接碳排放-能源间接排放-其他间接排放相结合的多层级碳排放核算模型,分析了我国铜产业各环节碳排放演变规律及碳中和实现机制。结果表明：①1980-2020年我国铜精矿、精炼铜、铜加工材、再生铜产品分别增长了6.6倍、 25.1倍、 88.5倍、 37.1倍,受碳中和目标实现对电力需求量增加的影响,预计2060年铜资源消费总量将较2020年提升62.3%,铜资源社会存量将达到3.9亿t,再生铜将于2030年超过原生铜成为主导资源类型。②2020年铜产业的碳排放总量达到2968.2万tCO₂e,其中,采选环节的吨铜碳排放量最高,达到了3.4tCO₂e,是第二位冶炼的2.3倍;冶炼环节的碳排放总量最大,达到铜产业的39.3%;再生环节的降碳效果突出,相较原生采选冶炼环节减少1251.2万tCO₂e;进出口贸易则进一步降低了该产业43.7%的碳排放总量。③预计2060年铜产业碳排放总量将达到1499.8万tCO₂e,通过促进国际贸易、循环经济、技术创新及环境市场建设等举措,可大幅降低产业的碳排放总量,其中国际贸易及循环经济情景的碳减排效果在2030年前均较显著、随后逐渐下降,技术创新及环境市场建设是该产业碳中和目标实现的根本,在2060年的减排潜力分别达到535.9万t及607.9万t。为了更好地促进该产业可持续发展及“双碳”目标实现,建议依托国内国际双循环格局合理调控铜产业结构,秉持全生命周期理念加快构建铜产业绿色供应链,紧随碳中和发展趋势促进资源循环减污降碳协同增效。     

The Essence of a Recycling Economy:Circular Utilization of Resources

By analyzing the relationship between a recycling economy and sustainable development theory, this article puts forward the basic concept of a recycling economy as a dynamic economic operational model, and explains the four basic characteristics. It is stressed that the essential element of a recycling economy is the use of resources circularly. In the end, this article analyzes the phenomena of utilizing the recycling economy concept incorrectly, and sets forth a number of problems that should be noted during the process of developing a recycling economy in China.     

循环冷却水处理中臭氧的杀菌作用

臭氧作为强氧化剂可以用于循环冷却水的处理中.试验研究了影响臭氧杀菌的基本因素,冷却水的pH和水温对处理效果基本没有影响.臭氧的杀菌能力取决于水中的剩余臭氧浓度,臭氧的消耗量与系统中的微生物数量有关.当水中剩余臭氧浓度为0.05mg/L和接触时间为14min时,可以使臭氧的灭菌力达99%.即在循环冷却水系统中,投加0.05mg/L臭氧,就可以控制系统中微生物的生长.由此确定了循环水处理过程中为控制系统中微生物的生长所需维持的最低臭氧浓度.     

Monitoring of soil biochemical quality parameters under greenhouse spinach cultivation through animal waste recycling

Under the intensive agricultural system, direct application of animal slurries to soils can provide a sustainable disposal of these wastes by inducing positive changes in soil quality and fertility. However, how animal wastes quantitatively affect the key nutrients (C, N, P and S) transforming soil enzymes is not clearly known. A greenhouse spinach cultivation study demonstrated that pig slurry, either in raw (RS) or processed (aerobically aged) (PS) form, significantly (p?β-glucosidase (23–39%), urease (59–103%), nitrate reductase (73–103%) and dehydrogenase (27–72%)) and microbial growth in soil as compared to the unamended control. However, it did not significantly (p?>?.05) alter the aryl sulphatase enzyme activity. Slurry applications also significantly improved the macro (N, P and K) and micronutrients (Cu, Mn, Zn and Fe) uptake by spinach plant and hence the yield (2.9–3.38 times higher than control). Similarly, compared to chemical fertilisers the application of pig slurries improved soil biological and biochemical parameters as well as plant nutrients uptake. This study demonstrated the closing of global energy and nutrient cycles through land application of animal wastes without compromising the crop yield.     

基于物质流分析的中国减物质化趋势及循环经济成效评价

物质流分析通过测量经济活动物质投入的数量、强度及其变化即物质化或减物质化趋势,能够反映可耗竭自然资源损耗和环境退化的总体情况,也是评价循环经济发展成效尤其是资源综合利用对物质消耗影响的一个有效工具。论文运用统计学和计量经济学方法,分析了中国2000-2013年直接物质投入及其与特定经济特征的关系,确定了资源利用强度变化趋势,评价了中国循环经济实践尤其是资源综合利用的成效。发现2000-2013年中国直接物质投入总量持续增加、单位GDP直接物质投入先上升后下降,说明中国已进入了相对的减物质化阶段;第二产业比重先增加后下降的变化趋势是直接物质投入强度变化的格兰杰原因;中国的资源综合利用总量增加但综合利用率仍很低,未对直接物质投入强度产生统计学意义上的显著影响;未来中国直接物质投入总量和人均值在很长时间内还将继续增加。     

Reuse of heavy metal-accumulating Cynondon dactylon in remediation of water contaminated by heavy metals

Phytoremediation technology is regarded as a simple and efficient way to remove heavy metals from contaminated soil. A reasonable disposal of metal hyperaccumulators is always and resource-saving. The a major issue in waste reuse heavy metal-accumulating Cynondon dactylon （L.） was investigated where heavy metals were desorbed by a facile acid-treatment. The result indicated that more than 90% of heavy metals （Zn, Pb and Cu） was extracted from Cynondon daetylon with 0.2 mmol· L^-1 HCl. The plant residue was used to adsorb heavy metals ions. The adsorption fitted the Langmuir isotherm model with the saturation adsorption capacity of 9.5 mg·g^-1 Zn^2＋, 36.2 mg·g^-1 Pb2＋ and 12.9 mg·g^-1 Cu^2＋, and the surface eomplexation and the backfilling of heavy metal imprinting cavities existed simultaneously during the adsorption. The treatment of wastewaters indicated that the plant residue exhibited a high removal rate of 97% for Cu. Also, the material could be recycled. The method offers a new disposal approach for heavy metal hyperaccumulator.     

居民电子废物回收行为影响因素的实证研究

基于对350名城市居民的问卷调查结果,运用验证性因子分析方法对居民的电子废物回收行为、行为意向及其影响因素进行了实证研究.结果表明,基于计划行为理论所建立的结构方程模型可以较为有效地诠释有关研究假设,环境知识、舆论宣传和垃圾分类等情境因素对电子废物回收行为具有调节作用.知觉行为控制对于行为意向转化为行为具有非常重要地促进作用,而便利状况则是影响知觉行为控制的重要因素.     

发展再生资源产业 实现可持续发展

党的十七届五中全会给再生资源产业的发展提供了重大发展机遇。再生资源行业必须坚持以科学发展为主题、以加快转变经济发展方式为主线,立足实际,转变经营方式,提高发展的全面性、协调性、可持续性,推动＂十二五＂期间再生资源产业发展迈上新台阶。     

嘉兴市电子废弃物回收体系公众调查与完善建议

嘉兴市地处长三角中心地带,是浙江电子废弃物的重要集散地之一。通过公众调查发现,嘉兴市电子废弃物产生量比较大,而现有电子废弃物回收体系主要是民间个体回收,公众对这种回收渠道的危害后果认知不足,从而造成正规回收渠道的回收困局。因此,应该借鉴浙江永康再生资源回收体系建设的经验,对个体户回收进行改造,并加强公众环保教育,建立合理责任承担机制,从而建设一套高效、环保和健康的电子废弃物回收体系。     

It's a dirty job but someone has to do it: The role of marine benthic macrofauna in organic matter turnover and nutrient recycling to the water column

Benthic macrofaunal populations through their feeding, bioturbation, burrow construction and sediment irrigation activities have profound influences on organic matter inputs to marine sediments (biodeposition) and on the vertical distribution of deposited organic matter within the sediment. These effects in turn influence the rates and pathways of organic matter mineralisation, and element cycles. Similarly, bioturbation, burrow construction and burrow irrigation are major determinants of sediment-water column fluxes of oxygen and nutrients.

In this review, I discuss the influences of the different benthic macrofaunal feeding (functional) groups on mineralisation processes and sediment-water column fluxes of particulate and dissolved nutrients. How these effects influence diagenic processes, the balance between aerobic and anaerobic processes, and the redox status of the surficial sediments. Finally, I discuss some of the limitations of the predominantly laboratory techniques which have been used to study “macrofaunal effects” and how this hinders the inclusion of the effects in quantitative sediment biogeochemical models.