二氧化碳的失汇

温室气体的大量排放所造成温室效应的加剧是全球变暖的基本原因。全球和区域碳循环已成为全球气候变化研究的重要内容之一。碳汇的巨大功能深受世人瞩目,影响碳汇增加因素的研究也越加必要。     

中国近海石油污染现状及防治

概述了本世纪初我国近海海域石油烃类污染状况，并对海洋环境中石油烃类的存在形式、源、汇以及转化过程作了详细介绍，讨论了石油污染对海洋的危害，论述了石油烃类污染分析防治的各种措施及其优缺点，提出了对当前和今后研究的一些建议。     

中国农田固碳减排发展现状及其战略对策

自20世纪80年代以来,农田固碳减排的动态变化日益成为全球的研究热点,它对于正确评价农业产业对全球气候变化的影响具有重要的理论意义。采取农业分区的方法,将我国划分为4个不同的农业区,并从区域植被覆盖、地理气候、品种、土壤性质、种植制度和施肥情况等方面,综合分析了各区域农田固碳减排的基本现状。通过对我国农田固碳减排的各个影响因素进行系统阐述,探明了耕作措施、水田种植面积、秸秆还田、施肥情况、轮作制度、土地利用方式和农田生态系统等是影响我国农田固碳减排的主要关键因素。同时,针对目前我国农田固碳减排的基本状况,提出了适合我国农田固碳减排的主要对策。文章认为,应从加强农田碳循环和土壤碳汇效应、合理调整农田土地利用结构、加强农田管理技术体系创新、加强农田生物固碳减排技术研究和注重降低农业生产温室气体的排放等方面开展系统研究,从而进一步增强农田的土壤固碳能力和减少温室气体的排放,达到我国农田固碳减排的最终目的。     

生物炭的环境效应及其应用的研究进展

作为新型环境功能材料,生物炭以其优良的环境效应和生态效应成为环境科学等学科研究的前沿热点.本文介绍了生物炭结构和基本特性,对其在土壤肥力改良、碳的增汇减排以及受污染环境修复的应用和机理方面的研究进展进行了综述,并扼要分析了生物炭研究的前景和方向,为生物炭技术的应用和推广提供一定的思路.     

长株潭城市群地类转移的碳传导效应与预测

土地利用碳排放是影响城市碳达峰、碳中和实现的重要因素.基于土地利用遥感数据和碳排放估算模型,得到长株潭城市群的土地利用碳排放量,借助转移矩阵分析了长株潭城市群土地利用转移的碳传导效应.此外,采用马尔科夫模型预测2030年和2060年的长株潭土地利用碳排放量.结果表明：①1995~2018年长株潭城市群土地利用净碳排放从810.84×10⁴ t增加到2015.41×10⁴ t,碳源/汇比整体呈上升趋势.其中,建设用地是主要的碳排放源,林草地是主要的碳汇.②不同时段地类转移引致的碳传导最终均表现为净碳排放,在时间上呈现先增加后减少的态势.其中以林地和耕地向建设用地转移产生的碳传导最为显著,涉及草地、水域和未利用地的碳传导效应微弱.③预测结果表明,长株潭城市群的土地利用碳排放预测量处于持续上涨态势,如若仍按目前趋势发展,则如期实现"双碳目标"存在难度.政府需要在加强林地的碳吸收能力以提升生态系统碳汇增量和遏制建设用地的无序扩张以减少碳源两方面着力,加快长株潭城市群的绿色低碳建设.上述结果为长株潭城市群开展低碳导向的城市土地利用调控提供了重要参考.     

Divergence in sink contributions to population persistence

Population sinks present unique conservation challenges. The loss of individuals in sinks can compromise persistence; but conversely, sinks can improve viability by improving connectivity and facilitating the recolonization of vacant sources. To assess the contribution of sinks to regional population persistence of declining populations, we simulated source–sink dynamics for 3 very different endangered species: Black‐capped Vireos (Vireo atricapilla) at Fort Hood, Texas, Ord's kangaroo rats (Dipodomys ordii) in Alberta, and Northern Spotted Owls (Strix occidentalis caurina) in the northwestern United States. We used empirical data from these case studies to parameterize spatially explicit individual‐based models. We then used the models to quantify population abundance and persistence with and without long‐term sinks. The contributions of sink habitats varied widely. Sinks were detrimental, particularly when they functioned as strong sinks with few emigrants in declining populations (e.g., Alberta's Ord's kangaroo rat) and benign in robust populations (e.g., Black‐capped Vireos) when Brown‐headed Cowbird (Molothrus ater) parasitism was controlled. Sinks, including ecological traps, were also crucial in delaying declines when there were few sources (e.g., in Black‐capped Vireo populations with no Cowbird control). Sink contributions were also nuanced. For example, sinks that supported large, variable populations were subject to greater extinction risk (e.g., Northern Spotted Owls). In each of our case studies, new context‐dependent sinks emerged, underscoring the dynamic nature of sources and sinks and the need for frequent re‐assessment. Our results imply that management actions based on assumptions that sink habitats are generally harmful or helpful risk undermining conservation efforts for declining populations.     

喀斯特常绿落叶阔叶混交林旱季CO2通量特征及其影响因子

对广西木论国家级自然保护区喀斯特常绿落叶阔叶混交林旱季生态系统CO₂净交换（NEE）的变化特征及其与环境因子的关系进行初步分析，计算研究期间碳汇大小，与其他相似气候条件下的不同生态系统进行对比，以期为准确估算该生态系统的年碳汇量提供基础。利用涡度相关法对该地区旱季（2018年10月1日~2019年3月31日）CO₂通量进行连续观测，同时开展降水量（P）、光合有效辐射（PAR）、空气温度（T_air）、土壤温度（T_soil）以及土壤含水量（SWC）等环境因子监测。观测期内该生态系统CO₂通量及浓度具有明显的"单谷"状日变化特征，白天表现为明显的碳汇，夜间则表现为明显的碳源，NEE在12：00最强，为-0.309±0.330 mg CO₂/（m²·s），18：30最弱，为0.074±0.061 mg CO₂/（m²·s）；观测期内NEE、生态系统呼吸（Re）、生态系统总生产力（GEP）分别为-121.4、209.2、330.6 g C/m²，该生态系统在2019年2月的碳吸收能力最强，Re、GEP在2018年10月达到最强；光合有效辐射是白天生态系统CO₂净交换（NEE_d）变化的主要控制因素（R²=0.40，p<0.01），空气温度与夜间生态系统CO₂净交换（NEE_n）存在指数关系（R²=0.1267，p<0.01）；观测期内的降雨抑制了该生态系统的碳汇能力，即降水对NEE产生了抑制作用。旱季该生态系统整体表现出明显的碳汇，碳汇值为1.214 t C/ha，明显低于相似气候条件下的其他生态系统。     

侵蚀逆境下土壤有机碳的迁移

土壤有机碳是陆地碳库的重要组成部分。土地利用和土地覆盖变化使得土壤中有机碳的含量发生很大的变化。土壤侵蚀是陆地碳库衰减的主要动力之一，也是陆地碳汇与海洋碳汇相互作用的重要过程。文章对土壤活性有机碳以及不同土地利用方式对土壤有机碳的影响作了介绍。     

氧化胁迫对沉水植物黑藻抗冷力的影响

以3种不同质量浓度的H2O2分别对沉水植物黑藻做3种不同程度的氧化胁迫预处理,再经冷胁迫后测定黑藻顶枝的膜脂过氧化程度(MDA含量)、细胞抗氧化酶(SOD,CAT)活性.结果发现低浓度氧化胁迫预处理(0.06mmol/L的H2O2浸泡4或6 h预处理组)的黑藻经冷胁迫处理后,成活率不降低,其膜脂过氧化程度和细胞抗氧化酶的活性还有提高;而经中、高浓度氧化胁迫预处理(0.60mmol/L的H2O2浸泡6和12 h预处理组或1.00mmol/L的H2O2浸泡4,6和12 h预处理组)后的黑藻在冷胁迫处理后的结果则相反.因此,沉水植物黑藻对氧化胁迫感知并做出反应的机制(氧化应激机制),在其对低温反应和适应过程中起着很重要的调节作用.建议早春时节在进行水生植物恢复过程中可采用适宜浓度的H2O2预处理植株,以提高植株的适应性和保持成活率,进一步提高水生植物恢复的效率和效果.     

Carbon Sequestration by Carbonization of Biomass and Forestation: Three Case Studies

We proposed the carbon sink project called “Carbon Sequestration by Forestation and Carbonization (CFC),” which involves biomass utilization and land conservation by incorporating the products of biomass carbonization into the agents for soil improvement, water purification, etc. Our purpose was to demonstrate the potential of the CFC scheme for carbon sequestration, particularly carbon storage in soil. Case studies were conducted in both developing and developed countries. 1. In southern Sumatra, Indonesia, 88,369 Mg-C year⁻¹ of wood residue from a plantation forest and excess bark from a pulp mill would be converted into 15,571 Mg-C year⁻¹ of the net carbon sink by biochar for soil improvement. The fixed carbon recovery of the system is 21.0%. 2. In a semiarid region in western Australia, the carbonization of wood residue was incorporated with multipurpose projects of a mallee eucalyptus plantation that involved the function of salinity prevention. During the project period of 35 years, the total carbon sink would reach 1,035,450 Mg-C with 14.0% by aboveground biomass, 33.1% by belowground biomass and 52.8% by biochar in soil. 3. In southern Kyushu, Japan, the study was focused on the effective use of surplus heat from a garbage incinerator for carbonizing woody materials. Sawdust of 936.0 Mg-C year⁻¹ would be converted into the net carbon sink of 298.5 Mg-C year⁻¹ by carbonization, with the fixed carbon recovery of the system being 31.9%. Consequently, the CFC project could encourage the creation of a carbon sink in soil. However, we recognize that the quality standard of biochar, the stability of biochar in soil, and the methods for monitoring biochar utilization must be clarified before incorporating biochar carbon into the carbon credit system. Throughout this article (except for diagrams and in citation details) carbonized biomass is, with the authors'agreement, called ‘biochar’ in lieu of the commonly used but misleading word ‘charcoal’ (Editor).