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1.
采用《固体废物浸出毒性浸出方法—水平振荡法》(HJ557-2010)对工业固体烧渣中重金属进行浸出试验研究,并利用火焰原子吸收分光光度法分别测定了其浸出液中的铅、铬、锌、镉、铜、铁和镍等7种重金属,用可见分光光度法测定砷,考察了模拟酸雨的pH值、液固比和浸取时间等因素对烧渣中重金属的浸出试验的影响,实验结果表明烧渣中各重金属的浸出值均未超出国家标准《危险废物鉴别标准—浸出毒性鉴别》(GB5085.3-2007)中的允许值,可直接作为建筑材料或路基材料使用。 相似文献
2.
黄河口不同恢复阶段湿地土壤N2O产生的不同过程及贡献 总被引:3,自引:1,他引:2
采用时空替代法,选择黄河口生态恢复前后未恢复区(R0)、2007年恢复区(R2007)和2002年恢复区(R2002)的芦苇湿地为研究对象,分析了生态恢复工程对湿地土壤N2O产生不同过程与贡献的影响.结果表明,尽管不同恢复阶段湿地土壤N2O总产生量差异明显,但总体均表现为N2O释放.恢复区湿地土壤的N2O产生量大于未恢复区.N2O的产生主要以硝化作用和硝化细菌反硝化作用为主,而反硝化作用对N2O的产生有较大削弱作用,这与不同恢复阶段湿地土壤理化性质密切相关.非生物作用对N2O产生量贡献较大,这与黄河口为高活性铁区,Fe的还原作用关系密切.尽管黄河口不同恢复阶段湿地土壤N2O的产生是生物作用与非生物作用共同作用的结果,但由于非生物作用对N2O产生的影响较大,应受到特别关注.温度和水分对不同恢复阶段湿地土壤N2O产生过程的影响不尽一致,这与土壤微生物活性对温度和水分的响应差异有关.黄河口不同恢复阶段湿地土壤的N2O总产生量介于(0.37±0.08)~(9.75±7.64)nmol·(kg·h)-1,略高于闽江口互花米草湿地的N2O总产生量,但明显低于富氧森林土壤、草原土壤和闽江口短叶茳芏湿地的N2O总产生量.研究发现,黄河口生态恢复工程的长期实施明显促进了N2O的产生,因而下一步生态恢复工程应统筹考虑景观恢复与温室气体削弱这两方面因素. 相似文献
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4.
闽江河口短叶茳芏湿地CH4和N2 O排放对氮输入的短期响应 总被引:5,自引:3,他引:5
利用静态箱-气相色谱法,研究了氮输入对闽江河口短叶茳芏湿地CH4和N2O排放通量的短期影响.结果表明,高氮输入在不同采样时间均促进了湿地CH4排放,低氮输入在不同时间则具有不同的变化特征.与对照处理相比,低氮和高氮2种处理分别使湿地CH4排放通量增加了-44.35%~1 057.35%和7.15%~667.37%.外源氮输入在24 h内对湿地N2O排放通量具有明显的正激发效应,最高可增加171.60倍和177.79倍,但在8 d后,氮输入对湿地N2O排放的激发效应减弱甚至消失.氮输入在短时间内对湿地土壤Ec、pH和Eh均未产生显著影响.湿地CH4排放通量在对照处理下仅与5 cm Eh存在显著负相关,在低氮处理下仅与10 cm地温呈显著负相关,在高氮处理下则与5 cm Ec、0、5 cm pH以及0、5、10 cm土壤Eh均呈显著相关性,而N2O排放通量在不同处理下与湿地气温、地温、盐度、pH和Eh等环境因子均不存在显著相关性.研究表明,探讨氮输入对湿地温室气体排放的影响应考虑其时间变异性. 相似文献
5.
The nitrogen (N) distribution and cycling of atmosphere-plant-soil system in the typical meadow Calamagrostis angustifolia wetland (TMCW) and marsh meadow Calamagrostis angustifolia wetland (MMCW) in the Sanjiang plain were studied by a compartment model. The results showed that the N wet deposition amount was 0.757 gN/(m2·a), and total inorganic N (TIN) was the main body (0.640 gN/(m2·a)). The ammonia volatilization amounts of TMCW and MMCW soils in growing season were 0.635 and 0.687 gN/m2, and the denitrification gaseous lost amounts were 0.617 and 0.405 gN/m2, respectively. In plant subsystem, the N was mainly stored in root and litter. Soil organic N was the main N storage of the two plant-soil systems and the proportions of it were 93.98% and 92.16%, respectively. The calculation results of N turnovers among compartments of TMCW and MMCW showed that the uptake amounts of root were 23.02 and 28.18 gN/(m2·a) and the values of aboveground were 11.31 and 6.08 gN/(m2·a), the re-translocation amounts from aboveground to root were 5.96 and 2.70 gN/(m2·a), the translocation amounts from aboveground living body to litter were 5.35 and 3.38 gN/(m2·a), the translocation amounts from litter to soil were larger than 1.55 and 3.01 gN/(m2·a), the translocation amounts from root to soil were 14.90 and 13.17 gN/(m2·a), and the soil (0-15cm) N net mineralization amounts were 1.94 and 0.55 gN/(m2·a), respectively. The study of N balance indicated that the two plant-soil systems might be situated in the status of lacking N, and the status might induce the degradation of C. angustifolia wetland. 相似文献
6.
SUN Zhi-gao~ 《环境科学学报(英文版)》2007,(8)
The nitrogen(N)distribution and cycling of atmosphere-plant-soil system in the typical meadow Calamagrostis angustifolia wetland (TMCW)and marsh meadow Calamagrostis angustifolia wetland(MMCW)in the Sanjiang plain were studied by a compartment model.The results showed that the N wet deposition amount was 0.757 gN/(m~2.a),and total inorganic N(TIN)was the main body (0.640 gN/(m~2.a)).The ammonia volatilization amounts of TMCW and MMCW soils in growing season were 0.635 and 0.687 gN/m~2, and the denitrification gaseous lost amounts were 0.617 and 0.405 gN/m~2,respectively.In plant subsystem,the N was mainly stored in root and litter.Soil organic N was the main N storage of the two plant-soil systems and the proportions of it were 93.98% and 92.16%, respectively.The calculation results of N turnovers among compartments of TMCW and MMCW showed that the uptake amounts of root were 23.02 and 28.18 gN/(m~2.a)and the values of aboveground were 11.31 and 6.08 gN/(m~2.a),the re-translocation amounts from aboveground to root were 5.96 and 2.70 gN/(m~2.a),the translocation amounts from aboveground living body to litter were 5.35 and 3.38 gN/(m~2.a),the translocation amounts from litter to soil were larger than 1.55 and 3.01 gN/(m~2.a),the translocation amounts from root to soil were 14.90 and 13.17 gN/(m~2.a),and the soil(0-15 cm)N net mineralization amounts were 1.94 and 0.55 gN/(m~2.a), respectively.The study of N balance indicated that the two plant-soil systems might be situated in the status of lacking N,and the status might induce the degradation of C.angustifolia wetland. 相似文献
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黄河口新生湿地土壤Fe和Mn元素的空间分布特征 总被引:4,自引:1,他引:4
2009年5月,在今黄河入海口北部的新生湿地区域,依据植被类型设置9个采样区,研究了不同植物群落下湿地土壤Fe和Mn含量的空间分布特征.结果表明,不同类型湿地土壤的Fe、Mn含量在水平分布上由三棱蔗草-朝天委陵菜湿地到光滩呈波动上升趋势,在垂直分布上则表现为不同的波动变化特征.成土母质决定湿地土壤Fe、Mn含量的空间分布,而海水、植被和土壤细颗粒对其也有重要影响.相关分析表明,Fe、Mn之间以及二者与粉粒、TN、NO-3-N和有机质呈极显著正相关(P<0.01),与黏粒呈显著正相关(P<0.05),说明Fe、Mn与N具有较好的共存性,土壤细颗粒和有机质是影响土壤Fe、Mn分布的主导因素.黄河口新生湿地的Fe含量范围为16.49~33.11 g·kg-1,均值为22.54 g·kg-1,与苏北潮滩湿地,中国黄土高原黄土和中国土壤的背景值相近,但略低于长江口湿地,红树林湿地和内陆湖泊湿地.Mn含量范围为305.87~711.39mg·kg-1,均值为451.09 mg·kg-1,低于中国黄土高原黄土和中国土壤的Mn含量背景值. 相似文献
8.
大别山五针松种群结构及动态研究 总被引:3,自引:0,他引:3
大别山五针松(Pinus dabeshanensis)是大别山区特有种,最大种群分布于安徽省岳西县大王沟。采用空间序列代替时间的方法分析种群结构,编制种群特定时间生命表,绘制死亡率曲线和消失率曲线,并用4个生存函数进行种群的生存分析;同时结合谱分析方法,分析了大别山五针松种群数量的动态变化。结果表明:大别山五针松种群数量少,结构存在波动性。幼苗阶段个体较丰富,幼树阶段个体较少,种群趋于衰退。种群死亡率和消失率曲线变化趋势基本一致,在第5龄级出现峰值。4个生存函数曲线表明,大别山五针松具有前期快速减少、中期稳定和后期衰退的特点。谱分析显示,大别山五针松种群动态除受基波影响外,还具有明显的小周期波动,谐波A3和A4处的周期波动与个体生长有关。 相似文献
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三江平原典型小叶章湿地土壤中硝态氮水平运移的模拟研究 总被引:8,自引:0,他引:8
选择三江平原小叶章湿地不同水分带上草甸沼泽土和腐殖质沼泽土2种土壤类型作为研究对象,以KNO3为示踪剂,模拟研究硝态氮在湿地土壤中的水平运移过程。结果表明,2种土壤各土层硝态氮水平运移浓度和速率均与运移距离呈极显著负相关(P〈0.01),并随运移距离增加呈一阶指数衰减曲线变化,各土层硝态氮水平运移速率主要受浓度梯度、水势梯度及土壤基质势的控制;土壤各土层中硝态氮水平运移速率与土壤含水量呈显著正相关(P〈0.05),并随土壤含水量增加呈指数增长曲线变化;土壤各土层中硝态氮水平运移浓度与土壤水分扩散率呈极显著正相关(P〈0.01),0—20cm土层硝态氮水平运移浓度随水分扩散率升高呈Boltzmann曲线变化,其他土层则呈指数增长曲线变化;草甸沼泽土比腐殖质沼泽土相应土层更利于硝态氮的水平运移,这主要与土层颗粒组成和孔隙度等物理性质的显著差异有关,而湿地水文条件可能对2种土壤物理性质的塑造有着重要影响。 相似文献
10.
三江平原不同土地利用方式下土壤硫含量变化特征 总被引:5,自引:0,他引:5
通过分析三江平原不同土地利用方式下土壤总硫、有效硫含量的变化,探明土壤硫含量演变特征。结果表明,小叶章湿地土壤总硫和有效硫含量高于开垦后的农田土壤,开垦导致土壤硫含量下降,且随着耕种年限的增加,土壤总硫和有效硫含量呈逐年下降趋势。弃耕7 a后土壤总硫和有效硫含量有所增加,但增加量相对较小,表明土壤硫库耗竭易、恢复难。土壤硫与有机质含量之间呈显著正相关关系,提示湿地开垦后土壤有机质含量降低可能是引起土壤硫肥力下降的主要因素,提高土壤有机质含量将有利于维持和提高农田土壤硫肥力。 相似文献