混交对亚热带针叶树根际土壤氮矿化和微生物特性的影响

混交阔叶树是退化红壤区针叶林改造的重要措施之一，土壤养分供应和转化是评价混交效应的重要参数，但混交后针叶树根际土壤氮矿化特征及其影响因素还不清楚。选取退化红壤区马尾松（Pinus massoniana Lamb.）纯林、湿地松（Pinus elliottii Engelmann）纯林及其补植木荷（Schima superba Gardn.et Champ.）形成的马-木混交林和湿-木混交林为研究对象，采集4种林分下针叶树根际土壤，测定速效养分含量、氮矿化速率、氮水解酶活性和微生物磷脂脂肪酸含量，探究混交对针叶树根际土壤氮供应及微生物特性的影响，分析土壤氮矿化和微生物特性间的相关性。结果表明：混交显著增加了针叶树根际土壤铵态氮，矿质氮和有效磷含量，而对硝态氮影响不显著。根际土壤氮矿化以硝化作用为主，混交后针叶树根际土壤氨化速率降低了27.0%，硝化速率增加了55.4%，而最终净氮矿化速率增加了24.1%。两个树种间，马尾松根际土壤矿质氮含量和净氮矿化速率显著高于湿地松。针叶树根际土壤真菌、丛枝菌根真菌，总微生物生物量及真菌/细菌比在混交后显著增加，且马尾松根际土壤总微生物和真菌生物量分别比湿地松高18.9%和27.0%。同时，针叶树根际土壤β-N-乙酰氨基葡萄糖苷酶活性在混交后显著增强，且根际土壤硝化速率和净氮矿化速率与微生物指标和酶活性正相关。总的来说，混交阔叶树显著提高了针叶树根际土壤氮供应，以此应对阔叶树混交后带来的养分竞争压力，而马尾松倾向于积极性的应对策略，通过增加土壤氮矿化以适应外界环境改变。     

Bioavailability of arsenic in soil and mine wastes of the Tamar valley,SW England

ABSTRACT

The southern part of the Tamar valley area in SW England is highly mineralised and mines in the region were the world's principal producers of tin, copper and arsenic during the mid nineteenth century. The Devon Great Consols Mine, covering 67.6 ha (167 acres) is situated in this area. Residues from the mining activity resulted in unvegetated spoil tips and local soils highly contaminated with As (range 120–52600 μg/g As). Sequential chemical extraction procedures were conducted on eight surface samples (0–15 cm) taken from a 2.0 km long transect from within the mine site to agricultural grassland. The proportion of water extractable As in agricultural top soils was lower (0.05–0.3%) than the values obtained for mine wastes (0.02–1.2%). Arsenic was found to be concentrated in the Fe-organic and residual fractions, which accounted for up 93 % of the total As in mine spoil and nearby soils.     

科尔沁沙地典型固沙人工林地土壤水分时空特征及其对环境因子的响应

土壤水分时空动态特征对于干旱地区人工林的可持续经营与管理起着至关重要的作用。以位于科尔沁沙地南缘的樟子松和柠条固沙人工林为对象，于2018年11月-2019年11月连续观测了林地0-200 cm土壤剖面的含水量、温度及微气象因子，系统分析了土壤水分的时空变化特征及其对环境因子的响应。研究期内，两种林地土壤水分的季节变化可分为冻结期、补充期、消耗期和稳定期；依据土壤剖面的水分特征可分为易变层、活跃层和稳定层，但两种林地的分层深度有一定差异。在生长季内（5-10月），土壤含水量对大气降雨的响应随着土层深度的增加而减弱；降雨对樟子松人工林0-20 cm层土壤水分的影响极显著（P<0.01），对柠条人工林0-10 cm层的影响极显著（P<0.01）、20-60 cm层显著（P<0.05）。在土壤冻融周期内（2018年11月-2019年4月），两种林地的土壤均表现为"单向冻结"和"双向融化"的特点；土壤温度是影响冻融期内土壤含水量的关键因素，两者呈极显著的指数函数关系；樟子松和柠条人工林土壤的最大冻结深度分别为170 cm和190 cm，前者10 cm土层解冻时间要比后者晚11 d，可能与乔木树冠的遮阴作用有关。潜在蒸散与柠条林0-60 cm层、樟子松林0-20 cm和200 cm层的土壤水分呈极显著相关（P<0.01），而与樟子松林60 cm和160 cm层呈显著相关（P<0.05），这与树木蒸腾和土壤蒸发等综合作用有关。研究表明，由于两种人工林的树种组成、树冠大小、郁闭程度和根系分布等结构特征不同会导致林地土壤水分时空特征的异质性及其对环境因素响应的差异。     

Temperature influences the interaction of ruminant PrPTSE with soil

Ovine scrapie and cervid chronic wasting disease can be transmitted in the absence of animal-to-animal contact, and environmental reservoirs of infectivity have been implicated in their spread and persistence. Investigating environmental factors that influence the interaction of disease-associated PrP with soils is imperative to understanding what is likely to be the complex role of soil in disease transmission. Here, we describe the effects of soil temperature on the binding/desorption and persistence of both ovine scrapie- and bovine BSE-PrP^TSE. Binding of PrP^TSE to a sandy loam soil at temperatures of 4°C, 8–12°C and 25–30°C demonstrated that an increase in temperature resulted in (1) a decrease in the amount of PrP^TSE recovered after 24 h of interaction with soil, (2) an increase in the amount of N-terminal cleavage of the prion protein over 11 d and (3) a decrease in the persistence of PrP^TSE on soil over an 18 mo period.     

气候和土地利用变化影响下生态屏障带水土流失趋势研究

受气候和地形等诸多因素影响，我国"两屏三带"国家生态屏障带中的川滇-黄土高原区域和南方丘陵带水土流失十分严重，自然灾害频发。但是，针对川滇-黄土高原区域和南方丘陵带水土流失时空格局变化，特别是未来气候变化和土地利用变化影响下水土流失变化趋势的研究很少。因此，本研究以川滇-黄土高原区域和南方丘陵带为研究对象，利用修正土壤流失方程（RUSLE）定量分析了该区在2000-2015年水土流失的时空变化规律及其影响因素，并预测了在RCP2.6和RCP4.5的未来气候情景下及土地利用变化条件下水土流失的变化趋势。研究结果表明：（1）黄土高原地区在植被恢复的积极作用下，水土流失显著缓解；（2）川滇地区的西南部因植被盖度的增长和降雨的减少水土流失显著缓解，但四川省境内人口密集区农田面积增加以及降水增加造成水土流失大幅度加剧；（3）南方丘陵带受降水增加影响导致了部分区域的水土流失恶化；（4）在未来气候变化情景下，由于大部分地区降雨将减少使土壤侵蚀趋于缓解，但四川、黄土高原和南方丘陵带大部分地区仍然面临未来农田面积增加带来的水土侵蚀压力。考虑到未来气候变化情景下降雨减少的趋势，建议在黄土高原地区提高草地在土地利用类型中的占比，在减少耗水量的同时维持地表盖度，缓解水土侵蚀；此外，各区域仍需控制农田面积，而且需通过加强坡耕地上保水保土耕作措施降低农田区域的土壤侵蚀压力。     

Variations of soil structure and microbial population in a compost amended soil

Changes in soil structure and in microbial population were recorded in a long term field experiment over the growing season of maize (June–November). Determinations were made on samples from plots which had received, for two years, the following treatments: mineral fertilizers, farmyard manure and three rates of compost. Seasonal variations were observed for the stability of soil aggregates, total porosity, pore size distribution, mycorrhizal infection and aerobic cellulolytic microorganisms. The stability of the soil aggregates changed in a similar way to that found for both mycorrhizal infection and the number of aerobic cellulolytic microorganisms. Physical characteristics were not affected in any instance by the organic dressings and microbiological populations were generally influenced only by the higher doses of compost.     

Microbial production and uptake of nitric oxide in soil

Abstract Fluxes of NO from three different soils have been studied by a flow-through system in the laboratory as a function of gas flow rate, of NO mixing ratio, and of incubation conditions. The dependence of net NO fluxes on gas flow rates and on NO mixing ratios could be described by a simple model of simultaneous NO production and NO uptake. By using this model, rates of gross NO production, rate constants of NO uptake, and NO compensation mixing ratios could be determined as function of the soil type and the incubation condition. Gross NO production rates were one to two orders of magnitude larger under anaerobic than under aerobic conditions. NO uptake rate constants, on the other hand, were only 5–8 times larger so that the compensation mixing ratios of NO were in a range of about 1600–2200 ppbv under anaerobic and of about 50–600 ppbv under aerobic conditions. The different soils exhibited similar NO uptake rate constants, but the gross NO production rate and compensation mixing ratio was significantly higher in an acidic (pH 4.7) sandy clay loam than in other less acidic soils. Experiments with autoclaved soil samples showed that both NO production and NO uptake was mainly due to microbial metabolism.