Streambank Soil and Phosphorus Losses Under Different Riparian Land‐Uses in Iowa1

Abstract: Phosphorus and sediment are major nonpoint source pollutants that degrade water quality. Streambank erosion can contribute a significant percentage of the phosphorus and sediment load in streams. Riparian land‐uses can heavily influence streambank erosion. The objective of this study was to compare streambank erosion along reaches of row‐cropped fields, continuous, rotational and intensive rotational grazed pastures, pastures where cattle were fenced out of the stream, grass filters and riparian forest buffers, in three physiographic regions of Iowa. Streambank erosion was measured by surveying the extent of severely eroding banks within each riparian land‐use reach and randomly establishing pin plots on subsets of those eroding banks. Based on these measurements, streambank erosion rate, erosion activity, maximum pin plot erosion rate, percentage of streambank length with severely eroding banks, and soil and phosphorus losses per unit length of stream reach were compared among the riparian land‐uses. Riparian forest buffers had the lowest streambank erosion rate (15‐46 mm/year) and contributed the least soil (5‐18 tonne/km/year) and phosphorus (2‐6 kg/km/year) to stream channels. Riparian forest buffers were followed by grass filters (erosion rates 41‐106 mm/year, soil losses 22‐47 tonne/km/year, phosphorus losses 9‐14 kg/km/year) and pastures where cattle were fenced out of the stream (erosion rates 22‐58 mm/year, soil losses 6‐61 tonne/km/year, phosphorus losses 3‐34 kg/km/year). The streambank erosion rates for the continuous, rotational, and intensive rotational pastures were 101‐171, 104‐122, and 94‐170 mm/year, respectively. The soil losses for the continuous, rotational, and intensive rotational pastures were 197‐264, 94‐266, and 124‐153 tonne/km/year, respectively, while the phosphorus losses were 71‐123, 37‐122, and 66 kg/km/year, respectively. The only significant differences for these pasture practices were found among the percentage of severely eroding bank lengths with intensive rotational grazed pastures having the least compared to the continuous and rotational grazed pastures. Row‐cropped fields had the highest streambank erosion rates (239 mm/year) and soil losses (304 tonne/km/year) and very high phosphorus losses (108 kg/km/year).     

Current Status of Marine Protected Areas in Latin America and the Caribbean

Abstract: Marine protected areas (MPAs), including no‐take marine reserves (MRs), play an important role in the conservation of marine biodiversity. We document the status of MPAs and MRs in Latin America and the Caribbean, where little has been reported on the scope of such protection. Our survey of protected area databases, published and unpublished literature, and Internet searches yielded information from 30 countries and 12 overseas territories. At present more than 700 MPAs have been established, covering more than 300,000 km² or 1.5% of the coastal and shelf waters. We report on the status of 3 categories of protection: MPAs (limited take throughout the area), MRs (no‐take throughout the area), and mixed‐use (a limited‐take MPA that contains an MR). The majority of protected areas in Latin America and the Caribbean are MPAs, which allow some or extensive extractive activities throughout the designated area. These 571 sites cover 51,505 km² or 0.3% of coastal and shelf waters. There are 98 MRs covering 16,862 km² or 0.1% of the coastal and shelf waters. Mixed‐use MPAs are the fewest in number (87), but cover the largest area (236,853 km², 1.2%). Across Latin America and the Caribbean, many biogeographic provinces are underrepresented in these protected areas. Large coastal regions remain unprotected, in particular, the southern Pacific and southern Atlantic coasts of South America. Our analysis reveals multiple opportunities to strengthen marine conservation in Latin America and the Caribbean by improving implementation, management, and enforcement of existing MPAs; adding new MPAs and MRs strategically to enhance connectivity and sustainability of existing protection; and establishing new networks of MPAs and MRs or combinations thereof to enhance protection where little currently exists.     

清江流域自然旅游资源调查与评价方法

根据清江流域自然旅游资源的特色，首先提出了一套对其进行详细系统的调查方法：（１）利用遥感数字图象处理技术及航、卫片解译结果，圈出潜在景区及潜在景点；（２）详细调查、收集及整理清江流域各市、镇已有资料，填写旅游资源调查登记卡片；（３）在（１），（２）基础上，对主要潜在景区及景点进行野外现场调研。然后，以调查结果为前提，提出了采用综合评分法，模糊数学评价方法，信息量评价方法，神经网络评价方法及地理信息     

山区农村居民点时空格局演变特征及蚁群仿真优化——以重庆澄江镇为例

山地农村居民点系统因受自然因素及人类活动等多重扰动而处于深刻转型中,探索山区农村居民点时空格局特征及其优化策略,对于优化山区国土空间格局、推进山区国土空间综合治理与乡村振兴具有重要意义。基于构建理论框架,集成运用景观格局指数法、栅格权重叠加评价法、改进蚁群算法（ACO）等,以重庆澄江镇为例,探索山区农村居民点时空格局演变特征及优化过程,提出优化调控策略。结果表明：（1）研究区农村居民点空间格局演变特征呈现集中、靠拢的演化发展趋势,总体呈现匀质、线状、向心、院落四种分布形态;同时高程、坡度、水域、城镇、道路、基础设施等自然—经济社会因素均对山区农村居民点时空格局演化产生重要影响。（2）改进蚁群算法优化后,研究区农村居民点斑块面积（CA）减少10.07%,居民点斑块数量（NP）和密度（PD）分别减少83.12%和81.16%,平均斑块面积（MPS）增加了4.3倍,平均最近邻体距离（MENN）增加了42.82%。优化后69.1%的农村居民点斑块都集中在适宜区和较适宜区内,且重点向交通便利、公共设施完善、生产便利和中心村庄集中。优化后的农村居民点空间格局更加紧凑有序,土地集约节约效率更高。（3）基于仿真优化结果,综合考虑村庄振兴“产业—人口—土地”互动耦合机制,提出城郊融合、产业集聚、景村融合、搬迁撤并四类农村居民点格局优化方案,助推山区乡村振兴。（4）优化结果同时表明改进的蚁群算法非常适用于复杂环境条件下的较小尺度要素空间布局优化,能够为山区国土空间规划编制提供技术支撑。     

干旱荒漠区人工绿洲土壤盐碱化风险综合评估与演变分析

为明晰干旱荒漠区人工绿洲水盐时空分异特征与盐碱化风险空间格局演变过程, 以甘肃省景电灌区为研究区, 以2002, 2010及2018年为研究代表年, 基于多级模糊理论从地质气候驱动、水土环境驱动和自然-人类驱动3个驱动过程构建土壤盐碱化风险评估体系, 集成云发生器原理、黄金分割率法、组合赋权法以及排队理论构建土壤盐碱化空间风险综合评价模型.将长序列监测数据、多时相空间数据以及经济社会数据依据各驱动要素权重以ArcGIS10.2为技术平台进行多源融合, 对各空间风险状态进行了空间可视化表达与流向追踪.结果表明: 1)研究区2002, 2010及2018年土地盐碱化整体风险分别为“临界状态”、“临界状态—轻度风险”、“轻度风险”; 2)地下水埋深及地下水矿化度是驱动土壤盐碱化进程加剧的主导因素; 3)灌区盐碱化空间风险演变模式剧烈程度排序为持续变化型>前期变化型>后期变化型>持续稳定型>反复变化型.研究区盐碱化整体风险状态呈现出由“无风险—临界状态”以及“临界状态—轻度风险”过渡的趋势; 4)2002~2018年间研究区盐碱化空间风险整体呈升级态势, 表征出明显的地区差异性且总体呈现由西北向东南以弧射状增高的空间格局.     

贫困退出背景下返贫脆弱性评价——融合区域与个体的新视角

精准识别返贫脆弱性,预防和化解返贫风险是“后扶贫时代”的工作重点。基于区域与个体尺度融合的新视角,运用BP神经网络法、熵值法和偏相关分析法对六盘山、秦巴山和大别山三大集中连片特困区进行返贫脆弱性评价与影响因素分析。研究发现：（1）三大集中连片特困区返贫脆弱度大致呈现由西向东递减的空间格局;（2）三个典型县区域和个体返贫脆弱性评价结果均显示古浪县>新县>栾川县;（3）高返贫风险县域中,高生态暴露度特征最为显著,而高返贫风险家庭中,生计动力不足特征最为明显;（4）区域返贫脆弱性主导因子为自然环境禀赋和经济发展水平,个体返贫脆弱性主导因子则为家庭劳动力综合素质、家庭收入、生计来源多样性、家庭成员健康状况和婚姻成本等。     

A novel approach for VOC source apportionment combining characteristic factor and pattern recognition technology in a Chinese industrial area

Volatile organic compound (VOC) emission control and source apportionment in small-scale industrial areas have become key topics of air pollution control in China. This study proposed a novel characteristic factor and pattern recognition (CF-PR) model for VOC source apportionment based on the similarity of characteristic factors between sources and receptors. A simulation was carried out in a typical industrial area with the CF-PR model involving simulated receptor samples. Refined and accurate source profiles were constructed through in situ sampling and analysis, covering rubber, chemicals, coating, electronics, plastics, printing, incubation and medical treatment industries. Characteristic factors of n-undecane, styrene, o-xylene and propane were identified. The source apportionment simulation results indicated that the predicted contribution rate was basically consistent with the real contribution rate. Compared to traditional receptor models, this method achieves notable advantages in terms of refinement and timeliness at similar accuracy, which is more suitable for VOC source identification and apportionment in small-scale industrial areas.     

晋中盆地主要城市冬季PM2.5传输特征分析

对2017～2019年晋中盆地主要城市PM₁₀和PM_2.5逐时浓度资料进行了分析,给出了晋中市和太原市颗粒物浓度主要分布特征;此外利用PM_2.5逐时浓度资料,结合HYSPLIT后向轨迹模型,通过轨迹密度分析（TDA）、轨迹停留时间分析（RTA）和潜在源贡献因子分析（PSCF）,并对PM_2.5逐时浓度资料和对应时刻风向数据进行分析,探讨了晋中盆地主要城市冬季PM_2.5传输特征.结果表明,太原市颗粒物浓度整体水平高于晋中市,月、季变化特征类似,均呈现冬季高,夏季低的特征,最高值出现在1月.晋中市受静稳型天气形势引起的颗粒物污染较受沙尘型天气形势导致的颗粒物污染相较太原市更普遍一些;颗粒物的分布呈现出晋中市中间值较多,太原市高值偏多、低值偏少的特点,冬季为晋中盆地PM_2.5污染高发季节.晋中盆地主要城市冬季PM_2.5传输通道均可分为4类：第一类通道沿太行山横谷传输,第二类通道为偏东南方向传输通道,第一、二类均为近距离传输通道,气团会携带较多...     

Characterizing a Major Urban Stream Restoration Project: Nine Mile Run (Pittsburgh,Pennsylvania, USA)

Urban stream restoration continues to be used as an ecological management tool, despite uncertainty about the long‐term sustainability and resilience of restored systems. Evaluations of restoration success often focus on specific instream indicators, with limited attention to the wider basin or parallel hydrologic and geomorphic process. A comprehensive understanding of urban stream restoration progress is particularly important for comparisons with nonurban sites as urban streams can provide substantial secondary benefits to urban residents. Here, we utilize a wide range of indicators to retrospectively examine the restoration of Nine Mile Run, a multi‐million dollar stream restoration project in eastern Pittsburgh (Pennsylvania, USA). Examination of available continuous hydrological data illustrates the high cost of failures to incorporate the data into planning and adaptive management. For example, persistent extreme flows drive geomorphic degradation threatening to reverse hydrologic connections created by the restoration and impact the improved instream biotic communities. In addition, human activities associated with restoration efforts suggest a positive feedback as the stream restoration has focused effort on the basin beyond the reach. Ultimately, urban stream restoration remains a potentially useful management tool, but continued improvements in post‐project assessment should include examination of a wider range of indicators.     

Climate adaptation of biodiversity conservation in managed forest landscapes

Conservation of biodiversity in managed forest landscapes needs to be complemented with new approaches given the threat from rapid climate change. Most frameworks for adaptation of biodiversity conservation to climate change include two major strategies. The first is the resistance strategy, which focuses on actions to increase the capacity of species and communities to resist change. The second is the transformation strategy and includes actions that ease the transformation of communities to a set of species that are well adapted to the novel environmental conditions. We suggest a number of concrete actions policy makers and managers can take. Under the resistance strategy, five tools are introduced, including: identifying and protecting forest climate refugia with cold-favored species; reducing the effects of drought by protecting the hydrological network; and actively removing competitors when they threaten cold-favored species. Under the transformation strategy, we suggest three tools, including: enhancing conditions for forest species favored by the new climate, but currently disfavored by forest management, by planting them at suitable sites outside their main range; and increasing connectivity across the landscape to enhance the expansion of warm-favored species to sites that have become suitable. Finally, we suggest applying a landscape perspective and simultaneously managing for both retreating and expanding species. The two different strategies (resistance and transformation) should be seen as complementary ways to maintain a rich biodiversity in future forest ecosystems.