后石油时代沙生灌木直燃发电对环境的影响＊

文章通过对内蒙古中西部地区沙生灌木的成分分析,基于生命周期法(LCA),定量论证了沙生灌木直燃发电开发模式对环境的影响和推广的可行性,指出相比石油等传统能源,这种模式具有较大的潜在效益,对于我国发展绿色替代能源,促进西部地区生态环境和经济协调发展具有一定的战略意义。     

川西北草原土壤硼、锰丰缺状况初探

根据110余个表层土壤样品硼、锰含量的测定结果和土壤缺乏硼、锰的临界值指标,探究了川西北草原土壤中硼、锰的有效性及其丰缺状况.结果表明,本区土壤中全硼全锰含量丰富分别达166.0ppm和736.6ppm,但有效硼和锰的含量仅分别为0.45ppm和5.11ppm,土壤缺乏硼和锰比较普遍.为该区推广施用硼、锰微肥提供了初步的科学依据.     

黑河中游边缘绿洲农田退耕还草的土壤碳、氮固存效应

研究黑河中游边缘绿洲农田退耕种植苜蓿5a后土壤碳、氮库的变化,通过对2个土类(开垦耕种的风沙土和灰棕漠土)退耕苜蓿地和相邻农田0～5、5～10和10～20cm土层土壤有机碳(SOC)和全氮(TN)、颗粒有机碳和氮(POC、PON)储量的分析表明:开垦耕种的风沙土和灰棕漠土有极低的SOC和TN含量,退耕种植苜蓿后0～20cm SOC储量提高了22.1%～27.8%,SOC的固存率平均为0.47 Mg/(hm²·a),0～5cm表层SOC储量变化最大,提高32%～66%;TN储量0～20cm储量变化不显著,在0～5cm表层TN储量风沙土和灰棕漠土分别提高12.8%和48.1%.退耕后POC和PON较SOC和TN有更显著的变化,其分配比例增加,0～20cm土层POC和PON储量分别提高22.8%～42.7%和18.6%～57.6%,在0～5cm变化最大;在瘠薄耕地转变为多年生苜蓿地后土壤C库的增加主要是由于POC的形成量增加.SOC含量相对更低的灰棕漠土比风沙土退耕后土壤C、N的增加更为明显.     

库布齐沙漠油蒿灌丛土壤呼吸速率时空变异特征研究

利用Li-840红外气体分析仪和Li-6400-09土壤呼吸气室组装而成的动态密闭土壤呼吸测定系统,于2006年生长季对内蒙古库布齐沙漠油蒿(Artemisia ordosica)生态系统2种不同类型土壤的土壤呼吸速率进行了野外测定,分析了日动态、季节动态及其对环境因子的响应,并阐述了油蒿灌丛空间异质性的特征.结果表明,油蒿灌丛的土壤呼吸速率日动态呈单峰曲线,在12:00左右有最大值.在适宜的水分和温度条件下,生长季里土壤呼吸速率在7～8月份出现最大值.土壤呼吸速率的季节动态与土壤含水量有显著的相关关系,表明水分是限制生长季干旱区灌丛土壤呼吸的最重要因子,分别可以解释油蒿冠幅下土壤和裸地的土壤呼吸速率2006年主要生长季节(5～9月)变化的75%和77%.油蒿灌丛土壤呼吸速率在空间尺度上存在着显著的异质性.油蒿冠幅覆盖下的土壤呼吸速率季节平均值为(155.58±15.20) mg·(m²·h)^-1,要显著地大于灌丛间裸地的数值(110.50±6.77) mg·(m²·h)^-1.2种不同类型土壤的土壤呼吸速率是由于根生物量的差异引起的,根生物量可以解释2006年生长季库布齐油蒿灌丛土壤呼吸速率空间异质性的43%.结果表明,在植被覆盖度异质性较大的灌丛生态系统中,要准确定量生态系统碳的释放时,必须充分考虑小尺度上土壤呼吸的空间异质性.     

城镇生活污水就近引浇防沙治沙工程林

城镇生活污水排入水体 ,严重影响水资源的使用价值。沙漠地区因缺水 ,造成许多地方造林失败。本文提出了将城镇生活污水就近引浇防沙治沙工程林的构想 ,并从经济和环境影响两个方面详细论述了该方案的比较优势     

退化草原碱蓬土壤微生物生物量的季节动态模型

研究了东北退化草原土壤微生物生物量的季节变化,生态因子的季节变化以及生态因子对土壤微生物生物量的综合作用规律,微生物生物量W和呼吸速率W1的季节动态呈单峰上凸式曲线变化,8月份的有明显的高峰值出现,其值为：w/mg g^-1=4.9,w1/mg g^-1d^-1=28.1,同时利用IRM模型研究了生态因子对土壤微生物生物量变化的综合作用规律;Mt △Mto[1 （0.21rn-w1)△t],生态因子对土壤微生物生长的综合作用指数rn在整个生长季节的变化范围为：0.0273-0.7264,其中7-8月份rn较大,对微生物生长的限制作用较小,微生物生长较快,5月、6月、9月和10月rn较小,对微生物生长的限制作用较大,微生物生长较慢。     

Desertification in the Sudan: causes,effects and policy options

Desertification is the spread of desert-like conditions in arid and semi-arid conditions. It is a result of pressure from both climatic and human factors. Desertification in the Sudan has been accelerating at a faster rate over the last two decades, leading to marginalization and the loss of arable land. The main factors contributing to desertification include drought, population growth, the spread of extensive agriculture, deforestation, rapid urbanization, the erosion of local political power, the lack of economic institutions and the absence of social institutions which have tended to reduce the capacity of the local people to cope with the resource degradation problem. Initiatives to arrest the desert encroachment must include improved cultivation methods, proper grazing management, reforestation and integration of livestock and crop production systems, coupled with good linkages to light processing industries.

This paper identifies the causal factors of desert encroachment, assesses its impact on the environment and humanity and concludes by recommending specific strategies to control the desert encroachment problem.     

The obtaining of biosphere reserve decrees in Mexico: analysis of three cases

SUMMARY

During eight years, the Biological Research Center of the Northwest promoted the federal decrees to attain legal protection of three key zones for biodiversity conservation in Mexico: La Sierra de La Laguna, El Desierto del Vizcaíno, and E1 Archipiélago Revillagigedo Biosphere Reserves. In this work, we discuss the biological and socioeconomical importance of these three regions, the necessary steps to attain a Presidential decree in Mexico, and the required strategies to promote local and political support for each decree. In a country like Mexico, the promotion of one Presidential decree to declare a zone as a biosphere reserve must successfully address two different goals: the technical and the political. The technical phase can be successfully completed by a research centre or university in 6 to 12 months; while the political phase may or may not be successfully completed. If successful, in our experience, it can be attained with 2 to 96 months of continuous efforts.     

Does low N-mineralisation rate in soils under grass help limit nitrate leaching in summer?

This paper aimed to confirm the hypothesis that rates of ammonification and net mineral-N production in soils under grass in summer are low and this, rather than nitrate uptake by plants, reduces mineral leaching from soils in summer. Six sets of soil samples were collected from under mown grass on the University of York campus in the UK. Samples were taken from two depths in late summer (August) and late autumn (November) to compare seasonal differences in N species transformations when field-moist soils were incubated for a week at ambient outdoor temperatures after prior removal of vegetation. Ammonification and net mineral-N production rates were low in August in spite of warm temperatures. Net mineral-N production rates were also low in November. The results agreed with those of an earlier study in a different year after considering weather differences between years. They support the hypothesis that litter accumulated over autumn/winter will be minimally mineralised and retain N before the temperature rises in spring. The study shows the merit of measuring concentrations of mineral-N species in both fresh soils and soils incubated at ambient outdoor temperatures after removing plant material to eliminate plant N uptake effects. The results suggest that soil C% and N% are more important than soil C:N ratio alone in understanding controls on N transformations.     

Changes in CO2 flux for different recovery processes of desertification in the alpine meadows of Northwest Sichuan北大核心CSCD

Desertification has emerged as a serious threat to the alpine meadows of Northwest Sichuan in recent decades. Artificial vegetation had certain effects on desertification recovery, while how the CO2 flux changed and its reasons are still unclear. During the growing season in 2016 (i.e., from July to September), we selected the desertified alpine meadows with different recovery degrees, including the early stage of restoration, the middle stage of restoration, the late stage of restoration, and control (the unrecovered desertification meadow) as four transects. CO2 flux was measured by the instrument LI-8100, and the microenvironment factors that affected CO2 flux changes were analyzed. The results showed that the carbon sequestration function of desertified alpine meadows gradually increased with the degree of recovery. Net ecosystem exchange (NEE) were -1.61, -3.55, and -4.38 μmol m-2 s-1 in the early, mid-term, and late transects, respectively, and the most dramatic changes occurred from the early stage to mid-term stage, increasing by 120.50%. Both ecosystem respiration (ER) and soil respiration (SR) were enhanced significantly with restoration (P < 0.05). In mid or late July, NEE, ER, and SR reached their maximum values, and thereafter, the indicators varied to near zero (P < 0.05). During the whole growing season, the daily dynamic in CO2 flux for the control alpine meadow was mild and retained the trend of continuous release all day, but that in the desertified alpine meadow was a single peak pattern. Moreover, with restoration process, the peak of CO2 flux increased and reached a peak in the late stage of the recovery process. The regression analysis showed that there was a significant positive correlation between CO2 flux and vegetation coverage, aboveground biomass, and soil moisture (0-5 cm) (P < 0.01), and a weak correlation with 0-5-cm soil temperature (P < 0.01). This indicates that topsoil moisture (5 cm) is a more significant factor for CO2 flux than topsoil temperature during the growing season in the restoration of desertified alpine meadows in Northwest Sichuan. In general, the vegetation recovery significantly improved the carbon-sequestration ability of the desertified alpine meadows during the growing season in Northwest Sichuan, and at the middle stage of restoration, the carbon-sequestration ability improved significantly due to vegetation restoration and increase in topsoil (0-5 cm) moisture. © 2018 Science Press. All rights reserved.