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151.
丛枝菌根真菌(AMF)对铯胁迫宿根高粱生长及根际土壤酶的影响 总被引:1,自引:0,他引:1
通过盆栽试验研究了接种透光球囊霉(Glomus diaphanum)、摩西球囊霉(Glomus mosseae)、地表球囊霉(Glomus versiforme)及幼套球囊霉(Glomus etunicatum)等4种丛枝菌根真菌(AMF)对铯污染下宿根高粱生长及根际土壤酶活性的影响.结果表明,与未接种对照相比,接种AMF处理均显著增加了宿根高粱的株高和根长,同时增强了过氧化氢酶、蔗糖酶活性及根系活力(P0.05),且以接种G.etunicatum增强效果最好,上述酶活性和根系活力分别相当于对照的1.11、2.25和4.04倍,而接种Glomus diaphanum最显著增强了酸性磷酸酶活性,使其提高了24.53 mg·g-1·d-1·FW(P0.05),宿根高粱对铯的耐性指数均高于对照,说明AMF在一定程度上能缓解铯污染胁迫对根际土壤酶的抑制作用,进而减轻核素铯对植物的毒害;接种AMF处理显著抑制了脲酶活性,表明脲酶可作为反应土壤核素铯污染的一个有效指标.同时也表明AMF有效地增强了宿根高粱对核素铯的耐性能力. 相似文献
152.
两种微藻胞外分泌物与NO2-、NO3-对2,4-D光解的影响 总被引:1,自引:1,他引:0
在模拟太阳光照射下,利用旋转式光化学反应装置,研究了海水小球藻(Chlorella vulgaris)和新月菱形藻(Nitzschia closterium)的胞外分泌物(EOM),以及分别在NO-2或(和)NO-3共存条件下对2,4-二氯苯氧乙酸(2,4-D)光解的影响.实验结果表明,2,4-D在海水小球藻和新月菱形藻EOM及分别在NO-2、NO-3共存下的光解过程均符合准一级动力学反应.研究发现,2,4-D的光解速率随海水小球藻和新月菱形藻EOM浓度的增加而减小,表明这两种微藻EOM可抑制海水中2,4-D的光解.当在微藻EOM溶液中分别加入不同浓度的NO-2或NO-3后,微藻EOM对2,4-D光解的抑制作用减弱,且随着NO-2和NO-3浓度的增加,2,4-D光解速率明显增加.特别是当微藻EOM与NO-2或NO-3三者共存时,可进一步促进2,4-D的光解. 相似文献
153.
好氧污泥颗粒化中胞外聚合物(EPS)的动态变化 总被引:1,自引:0,他引:1
在SBR中分别运行普通活性污泥和好氧颗粒污泥工艺,考察普通絮体污泥颗粒化过程中EPS的组分变化和分布情况.结果表明,通过减少沉淀时间可以获得质量高的颗粒污泥,污泥系统中的EPS可划分为紧密结合型、松散结合型和溶解性3种;普通污泥期、颗粒污泥初期和颗粒污泥稳定期的EPS含量均以紧密结合型EPS为主,颗粒污泥中总EPS和溶解性EPS含量均高于普通污泥,且颗粒形成初期溶解性EPS增长明显;颗粒污泥中紧密结合型EPS含量相对稳定,松散结合型EPS在不同污泥中含量很低,一个典型反应周期中蛋白质和多糖的变化趋势普遍是先降低后上升,普通污泥和颗粒污泥EPS中蛋白质含量均高于多糖,颗粒形成初期EPS中蛋白质含量有明显上升;普通絮体污泥中EPS和细菌分布均匀,颗粒污泥的表层聚集大量的细菌、内部主要成分是EPS. 相似文献
154.
155.
Sanchez-Hernandez JC Wheelock CE 《Environmental pollution (Barking, Essex : 1987)》2009,157(1):264-272
A laboratory-based study was conducted to determine the basal carboxylesterase (CbE) activity in different tissues of the earthworm Lumbricus terrestris, and its sensitivity to the organophosphate (OP) pesticide chlorpyrifos-oxon (CPx). Carboxylesterase activity was found in the pharynx, crop, gizzard, anterior intestine, wall muscle and reproductive tissues of L. terrestris, and multiple tissue-specific isozymes were observed by native gel electrophoresis. Esterase activity and sensitivity to CPx inhibition varied on a tissue- and substrate-specific basis, suggesting isoforms-specific selectivity to OP-mediated inhibition. Three practical issues are recommended for the use of earthworm CbE activity as a biomarker of pesticide exposure: (i) CbE should be measured using several routine substrates, (ii) it should be determined in selected tissues instead of whole organism homogenate, and (iii) earthworm CbE activity should be used in conjuncture with other common biomarkers (e.g., ChE) within a multibiomarker approach to assess field exposure of OPs, and potentially other agrochemicals. 相似文献
156.
Moreno B Vivas A Nogales R Macci C Masciandaro G Benitez E 《Environmental science and pollution research international》2009,16(3):253-264
Background, aim, and scope In this work, the potential for using olive-mill solid waste as an organic amendment for biochemical and biological restoration
of a trichloroethylene-contaminated soil, which has previously been stabilized through vermicomposting processes, has been
explored.
Materials and methods Trichloroethylene-contaminated water was pumped into soil columns with a layer of vermicompost at 10-cm depth (biobarrier
system). The impacts of the trichloroethylene on the microbial community were evaluated by determining: (1) the overall microbial
activity (estimated as dehydrogenase activity) and enzyme activities related to the main nutrient cycles (β-glucosidase, o-diphenoloxidase, phosphatase, urease, and arylsulphatase activities). In addition, isoelectric focusing of the soil extracellular
humic-β-glucosidase complexes was performed to study the enzymatically active humic matter related to the soil carbon cycle.
(2) The soil bacterial diversity and the molecular mechanisms for the bacterial resistance to organic solvents were also determined.
For this, polymerase chain reaction (PCR)-denaturing gradient gel electrophoresis (DGGE) was used to detect changes in bacterial
community structure and PCR-single-strand conformational polymorphism (SSCP) was developed and optimised for detection and
discrimination of the resistance-nodulation-division (RND) genes amplified from the contaminated soils.
Results Vermicompost reduced, with respect to the unamended soil, about 30% of the trichloroethylene leaching during the first month
of the experiment. Trichloroethylene had a marked negative effect on soil dehydrogenase, β-glucosidase, urease, phosphatase,
and arylsulphatase activities. Nevertheless, the vermicompost tended to avoid this toxic effect. Vermicompost also displays
stable humic-β-glucosidase complexes that increased the extracellular activity related to C-cycle in the contaminated soils.
The isoelectric focusing technique showed a more biochemically active humic matter in the soil sampled under the vermicompost.
The behaviour of the three main phyla of bacteria isolated from the DGGE bands was quite different. Bands corresponding to
Actinobacteria disappeared, whereas those affiliated with Proteobacteria remained after the trichloroethylene contamination. The disappeared Actinobacteria became visible in the soil amended with the vermicompost. Bands corresponding to Bacteriodetes appeared only in columns of contaminated soils. In this study, six types of RND proteins were detected by PCR-SSCP in the
natural soil, three in the trichloroethylene-contaminated soil and 7/5 in trichloroethylene-contaminated soil above/below
the vermicompost in the biobarrier columns. Trichloroethylene tended to reduce or eliminate all the clones detected in the
uncontaminated soil, whereas new efflux pumps appeared in the biobarrier columns.
Discussion Although enzymes incorporated into the humic substances of vermicomposted olive wastes are quite stable, trichloroethylene
also inhibited the background levels of the soil extracellular β-glucosidase activity in the amended soils. The decrease was
less severe in the biobarrier system, but in any case, no relation was found between the levels of trichloroethylene in soil
and extracellular β-glucosidase activity, or between the latter and the quantity of humic carbon in soils. The isoelectric
focusing technique was carried out in the humic fraction to determine whether the loss of activity occurred in overall extracellular
β-glucosidase or in that linked to stable humic substances (humic–enzyme complexes). The contaminated soils showed the lower
enzyme activities, whereas contaminated and amended soils presented greater quantity of focalised (and therefore stable) humic
carbon and spectra heterogeneity: very different bands with higher enzyme activities. No clear relationship between trichloroethylene
concentration in soil and diversity of the bacterial population was noted. Similar patterns could be found when the community
structures of bacteria and microbial activity were considered. Since the use of the dehydrogenase assay has been recognised
as a useful indicator of the overall measure of the intensity of microbial metabolism, these results could be attributed to
PCR-DGGE methodology, since the method reveals the presence of dominant populations regardless of their metabolic state. Trichloroethylene
maintained or even increased the number of clones with the DNA encoding for RND proteins, except for the contaminated soil
located above the vermicompost. However, the main effect of trichloroethylene was to modify the structure of the community
in contaminated soils, considering the type of efflux pumps encoded by the DNA extracted from soil bacteria.
Conclusions Trichloroethylene inhibited specific functions in soil and had a clear influence on the structure of the autochthonous bacterial
community. The organic matter released by the vermicomposted olive waste tended to avoid the toxic effect of the contaminant.
Trichloroethylene also inhibited the background levels of the soil extracellular β-glucosidase activity, even when vermicompost
was present. In this case, the effect of the vermicompost was to provide and/or to stimulate the humic-β-glucosidase complexes
located in the soil humic fraction >104, increasing the resistance of the enzyme to the inhibition. The bacterial community from the soil presented significantly
different mechanisms to resistance to solvents (RND proteins) under trichloroethylene conditions. The effect of the vermicompost
was to induce these mechanisms in the autochthonous bacterial community and/or incorporated new bacterial species, able to
grow in a trichloroethylene-contaminated ambient. Coupled biochemical and molecular methodologies are therefore helpful approaches
in assessing the effect of an organic amendment on the biochemical and biological restoration of a trichloroethylene-contaminated
soil.
Recommendations and perspectives Since the main biochemical and biological effects of the organic amendment on the contaminated soil seem to be the incorporation
of biochemically active humic matter, as well as new bacterial species able to grow in a trichloroethylene-contaminated ambient,
isoelectric focusing and PCR-SSCP methodologies should be considered as parts of an integrated approach to determine the success
of a restoration scheme. 相似文献
157.
卤代酚复合污染对鲤科金鱼的生化毒性效应研究 总被引:1,自引:0,他引:1
为探讨卤代酚复合污染对水生生物的联合毒性效应,探究较为可靠的检测方法,根据所选6种卤代酚化学结构的相似程度和48 h LC50值,将其分为3组二元混合物进行急性暴露实验, 毒性单位比为1∶1,每组分2个浓度级别观察金鱼生物学行为的变化,同时检测金鱼肝脏中3种抗氧化酶(SOD,CAT和GSH-Px)活性以及酶活性影响率的变化. 结果表明:3组卤代酚对金鱼肝脏中3种抗氧化酶的酶活性影响率变化均有显著性差异(P<0.01);3种抗氧化酶中仅SOD在1/2LC50剂量暴露组中均表现为明显升高的酶活性激活率或酶活性抑制率,提示SOD较适合作为卤代酚低浓度复合水污染情况监测的生物化学检测指标. 相似文献
158.
胞外多聚物在好氧颗粒污泥形成中的作用机制 总被引:31,自引:13,他引:18
在SBR反应器活性污泥好氧颗粒化过程中,分析不同时期污泥EPS主要成分的变化、污泥表面特性的变化及二者相关关系.不同时期污泥样品胞外蛋白的SDS-PAGE表明,蛋白分子量条带主要分布在(31.0~97.4)×103,与种泥相比,颗粒污泥在形成过程中增加了一些新蛋白条带,且条带颜色逐渐变深,定性表明蛋白种类及含量的增加.定量测定也表明,胞外蛋白分泌量随颗粒污泥的形成逐渐从49.4 mg·g-1增至148.3 mg·g-1,多糖则无明显变化,蛋白/多糖值也从2.3逐渐增至4.9.颗粒污泥表面疏水性比种泥约增加1倍,疏水性的变化与蛋白/多糖值正相关,相关系数为0.969.测得种泥与颗粒污泥表面Zeta电位平均值分别为-28.5 mV和-13.2 mV,颗粒污泥表面的电负性明显降低.由蛋白质自身特性,可推测其通过增加污泥表面相对疏水性和降低污泥表面电负性而促进好氧颗粒污泥形成的作用机制. 相似文献
159.
160.
研究了在十二烷基苯磺酸钠(SDBS)和多聚磷酸钠(STPP)及其复合胁迫下,黑藻过氧化物酶(POD)、过氧化氢酶(CAT)、超氧化物歧化酶(SOD)活性变化及其耐受浓度.结果表明,POD活性随着处理浓度的增加而逐渐增大;CAT在低浓度胁迫时活性逐渐增加,在较高浓度胁迫时活性降低;实验初期(6h时),SOD活性逐渐升高,随着SDBS处理浓度的提高及时间延长,SOD活性下降,并且在8mg/L浓度处理72h,SOD失活.SDBS对黑藻SOD的抑制作用大于STPP.黑藻对SDBS的耐受浓度(8mg/L)明显小于STPP的耐受浓度(256mg/L).黑藻对SDBS和STPP复合胁迫的耐受浓度值为(32+64)mg/L. 相似文献