半干半湿法烟气脱硫技术研究

在实验的基础上,分析了半干半湿法烟气脱硫技术的优点。根据影响该技术脱硫效率的主要因素,通过实验,较系统地研究了温距与喷嘴布局、入塔烟温、Ca/S摩尔比、脱硫灰循环利用等对脱硫效率的影响,并对脱硫灰制砖的成分配制也进行了讨论。结果表明,在整体Ca/S摩 尔比为1.5～1.7时,该技术工艺可以达到80%以上的脱硫效率。      

半干旱区人工封育草场植被群落生态位研究——以宁夏盐池县长期定位监测点为例

人工封育是草场恢复和重建的一种主要措施。为研究半干旱区人工封育草地植物种群生态位,以宁夏盐池县人工封育区3种不同处理方式（长期完全封育、短期完全封育、短期不完全封育）为研究对象,将封育区分为封育核心区（E区）、封育边缘区（E1区）和封育外围区（E2区）,通过分析在该地区出现的27种植物种群的Levins生态位宽度指数和Pianka生态位重叠指数,揭示植物种群生态位在干旱荒漠环境下的变化规律,为进一步分析该地区群落稳定性提供依据。研究结果表明：1）核心区和外围区生态位宽度最大的都是刺沙蓬Salsola ruthenica lljin,分别为0.832和0.810,而边缘区生态位宽度最大的是丝叶山苦荬Lxeris chinensis var.graminifolia,为0.742,这2种植物的生物学特性决定了它们能够很好的适应封育区的环境,并很好的利用封育区的资源,结果是它们的生态位宽度明显高于其他物种。2）对三区内不同植物种群的生态位宽度分析结果显示,三区的群落稳定性表现为E1区〉E2区〉E区;长期的完全封育并不利于封育区内植物群落的稳定;而短期的完全封育措施比不完全封育措施更有利于植被群落的稳定。3）通过分析三区内不同植物种之间的生态位重叠得出,E区生态位重叠最大值出现在草地风毛菊Saussurea amara、苦豆子Sophora alopecuroides L、沙芦草Agropyron mongolicum Keng与臭蒿Artemisia hedinii之间,都是0.98。E1区生态位重叠最大值是达乌里胡枝子Lespedeza davurica和草木樨状黄芪Astragalus melilotoides之间（0.82）。E2区生态位重叠最大的一对是草木樨状黄芪和冰草Agropyron cristatum（0.99）。相关分析表明：生态位宽度与生态位重叠之间并没有明确的线性关系。生态位宽度窄的物种之间可能有较高的生态位重叠,反之,则较低,但并不是完全如此。     

ICP-MS半定量分析在应急监测中的应用研究

利用ICP-MS半定量分析对应急监测水样进行全谱图扫描,初步判断质量范围6~260的所有重金属离子及其同位素的浓度,快速找到主要重金属污染物。该方法简单、快捷,不受标准物质使用限制,预处理方法简单,测定值与标准值的相对误差结果小于±30%。通过及时更新半定量响应因子曲线,可使半定量结果更为准确,为进一步准确定量提供可靠浓度范围。对应急监测过程中的复杂基体水样、未知水样的分析具有实际意义。通过分析企业的重金属排放浓度,可用于判定企业偷排漏排现象。     

Thresholds of species loss in Amazonian deforestation frontier landscapes

In the Brazilian Amazon, private land accounts for the majority of remaining native vegetation. Understanding how land‐use change affects the composition and distribution of biodiversity in farmlands is critical for improving conservation strategies in the face of rapid agricultural expansion. Working across an area exceeding 3 million ha in the southwestern state of Rondônia, we assessed how the extent and configuration of remnant forest in replicate 10,000‐ha landscapes has affected the occurrence of a suite of Amazonian mammals and birds. In each of 31 landscapes, we used field sampling and semistructured interviews with landowners to determine the presence of 28 large and medium sized mammals and birds, as well as a further 7 understory birds. We then combined results of field surveys and interviews with a probabilistic model of deforestation. We found strong evidence for a threshold response of sampled biodiversity to landscape level forest cover; landscapes with <30–40% forest cover hosted markedly fewer species. Results from field surveys and interviews yielded similar thresholds. These results imply that in partially deforested landscapes many species are susceptible to extirpation following relatively small additional reductions in forest area. In the model of deforestation by 2030 the number of 10,000‐ha landscapes under a conservative threshold of 43% forest cover almost doubled, such that only 22% of landscapes would likely to be able to sustain at least 75% of the 35 focal species we sampled. Brazilian law requires rural property owners in the Amazon to retain 80% forest cover, although this is rarely achieved. Prioritizing efforts to ensure that entire landscapes, rather than individual farms, retain at least 50% forest cover may help safeguard native biodiversity in private forest reserves in the Amazon. Umbrales de Pérdida de Especies en los Paisajes Fronterizos de Deforestación en el Amazonas Ochoa‐Quintero     

Mapping opportunities and challenges for rewilding in Europe

Farmland abandonment takes place across the world due to socio‐economic and ecological drivers. In Europe agricultural and environmental policies aim to prevent abandonment and halt ecological succession. Ecological rewilding has been recently proposed as an alternative strategy. We developed a framework to assess opportunities for rewilding across different dimensions of wilderness in Europe. We mapped artificial light, human accessibility based on transport infrastructure, proportion of harvested primary productivity (i.e., ecosystem productivity appropriated by humans through agriculture or forestry), and deviation from potential natural vegetation in areas projected to be abandoned by 2040. At the continental level, the levels of artificial light were low and the deviation from potential natural vegetation was high in areas of abandonment. The relative importance of wilderness metrics differed regionally and was strongly connected to local environmental and socio‐economic contexts. Large areas of projected abandonment were often located in or around Natura 2000 sites. Based on these results, we argue that management should be tailored to restore the aspects of wilderness that are lacking in each region. There are many remaining challenges regarding biodiversity in Europe, but megafauna species are already recovering. To further potentiate large‐scale rewilding, Natura 2000 management would need to incorporate rewilding approaches. Our framework can be applied to assessing rewilding opportunities and challenges in other world regions, and our results could guide redirection of subsidies to manage social‐ecological systems.     

Assessing intervention effectiveness at promoting voluntary conservation practice adoption in agrienvironments

Although implementing conservation practices on private farms and forests can produce substantial environmental benefits, these practices are not being adopted widely enough to result in measurable improvements at regional scales. Researchers have investigated the production and program factors influencing producer choices to voluntarily adopt these practices. However, the findings of reviews are inconsistent, raising questions about review methods, including the omission of relevant variables. Further, applying lessons from past work to promote adoption is difficult because many reviews investigated dispositional or demographic variables that practitioners and policy makers cannot directly observe or influence. We conducted a new review of 146 empirical studies that tested the effects of different interventions (e.g., financial incentives, outreach events, and nudges) on increasing the likelihood of producers adopting conservation practices. We conducted a metaregression of quantitative studies from diverse disciplines that filtered studies by quality (i.e., use of randomization and clear analysis reporting). We synthesized these results with a thematic analysis of qualitative studies on producer perspectives about conservation practices. Financial incentives had the strongest evidence of increasing producers’ likelihood of adopting conservation practices (odds ratio 1.86, p < 0.05). However, this effect was only apparent after filtering by study quality, which also improved model fit and identified significant regional differences (odds ratio –1.69, p < 0.01). The thematic review of qualitative studies revealed that peer groups may be successful in reinforcing adoption behaviors due to homophily effects and that financial incentives not only offset implementation costs but also mitigated perceived risks of adoption. Given the problems we encountered in testing hypotheses about the magnitude of variability explained by intervention types and practice characteristics, we recommend additional experimental and longitudinal work that accounts for financial incentives and pairs qualitative and quantitative data to clarify relationships between program design and practice adoption rates.     

Global rarity of intact coastal regions

Management of the land–sea interface is essential for global conservation and sustainability objectives because coastal regions maintain natural processes that support biodiversity and the livelihood of billions of people. However, assessments of coastal regions have focused strictly on either the terrestrial or marine realm. Consequently, understanding of the overall state of Earth's coastal regions is poor. We integrated the terrestrial human footprint and marine cumulative human impact maps in a global assessment of the anthropogenic pressures affecting coastal regions. Of coastal regions globally, 15.5% had low anthropogenic pressure, mostly in Canada, Russia, and Greenland. Conversely, 47.9% of coastal regions were heavily affected by humanity, and in most countries (84.1%) >50% of their coastal regions were degraded. Nearly half (43.3%) of protected areas across coastal regions were exposed to high human pressures. To meet global sustainability objectives, all nations must undertake greater actions to preserve and restore the coastal regions within their borders.