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31.
Hopanoids are pentacyclic triterpenoid lipids occurring in bacteria. They are synthesized from isopentenyl units which are
formed in a new biosynthetic route leading to isopentenyl diphosphate. Six C5 units are joined to form squalene, the immediate precursor in hopanoid synthesis. In a highly complex cyclization reaction
that shares considerable similarities with that of oxidosqualene to sterols, the hopane skeleton is formed from squalene by
the squalene-hopene cyclase. Recent elucidation of the X-ray structure of this membrane-bound cyclase has shed some light
on the properties of this unusual enzyme. The active site is located in a cavity within the enzyme. The squalene substrate
diffuses through a channel structure from the membrane into this cavity and is there transformed into hopene. Polar side chains
are attached to hopene resulting in the amphiphilic molecular structure of many hopanoids. These hopanoids are membrane components
involved in regulating membrane fluidity and stability. However, the many structural variants of hopanoids indicate that they
may have other interesting but as yet unknown functions. 相似文献
32.
We have determined the activity of alkaline phosphatase in chorionic villous tissue obtained in the first trimester of pregnancy, in order to obtain the normal range of values as a prerequisite for application to the prenatal diagnosis of the rare bone disease hypophosphatasia. The activities found were a combination of intestinal and liver/bone/kidney types; traces of placental type were present in only one sample. 相似文献
33.
34.
Heinz Rüdel Winfried Schröder Karl Theo von der Trenck Gerhard Andreas Wiesmüller 《Environmental science and pollution research international》2009,16(5):486-498
Background Due to the requirements of the EU Water Framework Directive and other legal regulations (e.g., national laws like the German
Federal Soil Protection Act), but also due to the implementation of the new EU chemicals management system REACH, environmental
monitoring will gain increasing importance for the surveillance of environmental quality as well as for the assessment of
chemicals. Against this background, the Work Group on ‘Environmental Monitoring’ of the Division of ‘Environmental Chemistry
and Ecotoxicology’ within the German Chemical Society has compiled a position paper on substance-related environmental monitoring.
Scope Core elements of this position paper are the definitions of important terms like monitoring, exposure monitoring, effect monitoring,
and integrated monitoring. Moreover, temporal and spatial aspects (monitoring of spatial distributions, trend monitoring,
and retrospective monitoring) and their applications are discussed. The main focus of this position paper is the coverage
of aspects which have to be observed for the preparation and implementation of a monitoring program. Essential is the clear
specification of the targets of the monitoring which determine the development of the monitoring concept and its realization,
e.g., if environmental media (compartments) or organisms are most appropriate as samples for the aim of the study. Of course,
also the properties of the target substances are important (e.g., lipophilicity/bioaccumulation as pre-requisite for an exposure
monitoring with organisms). Finally, the monitoring phases of sample planning, sampling, storage and transport of samples,
selection of analytical methods, quality assurance measures as well as reporting are discussed.
Perspectives An important issue for the future is to link the quantification of chemicals in environmental compartments (exposure and pollution
monitoring) more closely to the study of biological effects (effect monitoring) than has been the case up to now. Furthermore,
by inclusion of a spatial differentiation, a comprehensive evaluation of the state of an ecosystem can be obtained and the
relevance of the results improved. Practical examples of monitoring studies which illustrate various aspects covered in this
position paper will be presented in a series of publications by members of the Work Group in the following issues of this
journal.
相似文献
Gerhard Andreas WiesmüllerEmail: |
35.
Erik R Coats Frank J Loge Michael P Wolcott Karl Englund Armando G McDonald 《Water environment research》2007,79(12):2396-2403
Biologically derived polyesters known as polyhydroxyalkanoates (PHAs) represent a potentially "sustainable" replacement to fossil-fuel-based thermoplastics. However, current commercial practices that produce PHA with pure microbial cultures grown on renewable, but refined, feedstocks (i.e., glucose) under sterile conditions do not represent a sustainable commodity. Here, we report on PHA production with a mixed microbial consortium indigenous to an activated sludge process on carbon present in municipal wastewaters. Reactors operated under anaerobic/aerobic and aerobic-only mode and fed primary solids fermenter liquor maintained a mixed microbial consortium capable of synthesizing PHA at 10 to 25% (w/w), while reducing soluble COD by approximately 62 to 71%. More critically, an aerobic batch reactor seeded from the anaerobic/aerobic reactor and fed fermenter liquor achieved approximately 53% PHA (w/w). Results presented suggest that environmentally benign production of biodegradable polymers is feasible. We further used PHA-rich biomass to produce a natural fiber-reinforced thermoplastic composite that can be used to offset advanced wastewater treatment costs. 相似文献
36.
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38.
环境中类固醇激素具有很高的生物活性,在水环境中又普遍存在,因而对鱼类健康造成威胁。目前,对鱼体内类固醇激素的吸收过程和毒代动力学知之甚少,特别是其中细胞膜转运体的作用。我们考察了17种内源性和环境中类固醇激素与斑马鱼体内有机阴离子摄取性转运体Oatp1d1的相互作用,Oatp1d1在斑马鱼的肝脏和肾脏中有显著表达。我们选择了不同类别的类固醇激素,包括雄烯二酮(A4)、黄体酮(P4)及其代谢物、糖皮质激素和螺旋内酯甾酮(竞争性抑制萤光黄(Lucifer Yellow, LY)的吸收)。半数抑制效应浓度(IC50)通过S形抑制曲线获得,P4的IC50最小,其他IC50由大到小排列为:17α-羟基黄体酮>丙酸氯倍他索>螺旋内酯甾酮>21-羟基黄体酮>醋酸氟氢可的松和其他的糖皮质激素。类固醇激素的亲脂性与Oatp1d1相互作用的活性呈正相关关系。我们的数据表明不同类别的类固醇激素与Oatp1d1的相互作用活性不同,或为吸收,或为抑制,或吸收和抑制。如此可知类固醇激素会介入内源性底物的转运过程,以致相关的生理过程。同时,类固醇激素可通过竞争性抑制作用改变环境污染物的细胞贩运。
精选自Raffael Alois Willi, Karl Fent. Interaction of environmental steroids with organic anion transporting polypeptide (Oatp1d1) in zebrafish (Danio rerio). Environmental Toxicology and Chemistry,2018,37:2670-2676.
详情请见 https://doi.org/10.1002/etc.4231 相似文献
39.
András Bardossy Arne Färber Steffen Schönau Bernhard Westrich Thomas Jancke Gerhard Schmid Sven Wurms Karl Stahr Thomas Gaiser Harald Frauenknecht Thilo Streck Joachim Ingwersen Claudia Kreschnak Ulrich Kern Hilke Heppelmann Ekkehard Christoffels Ulrich Förstner Patrick Jacobs 《Environmental Sciences Europe》2006,18(1):67-69
40.
Lesley K Smith Mary A Voytek John Karl B?hlke Judson W Harvey 《Ecological applications》2006,16(6):2191-2207
Rates of benthic denitrification were measured using two techniques, membrane inlet mass spectrometry (MIMS) and isotope ratio mass spectrometry (IRMS), applied to sediment cores from two NO3(-)-rich streams draining agricultural land in the upper Mississippi River Basin. Denitrification was estimated simultaneously from measurements of N2:Ar (MIMS) and 15N[N2] (IRMS) after the addition of low-level 15NO3- tracer (15N:N = 0.03-0.08) in stream water overlying intact sediment cores. Denitrification rates ranged from about 0 to 4400 micromol N x m(-2) x h(-1) in Sugar Creek and from 0 to 1300 micromol N x m(-2) x h(-1) in Iroquois River, the latter of which possesses greater streamflow discharge and a more homogeneous streambed and water column. Within the uncertainties of the two techniques, there is good agreement between the MIMS and IRMS results, which indicates that the production of N2 by the coupled process of nitrification/denitrification was relatively unimportant and surface-water NO3- was the dominant source of NO3- for benthic denitrification in these streams. Variation in stream NO3- concentration (from about 20 micromol/L during low discharge to 1000 micromol/L during high discharge) was a significant control of benthic denitrification rates, judging from the more abundant MIMS data. The interpretation that NO3- concentration directly affects denitrification rate was corroborated by increased rates of denitrification in cores amended with NO3-. Denitrification in Sugar Creek removed < or = 11% per day of the instream NO3- in late spring and removed roughly 15-20% in late summer. The fraction of NO3- removed in Iroquois River was less than that of Sugar Creek. Although benthic denitrification rates were relatively high during periods of high stream flow, when NO3 concentrations were also high, the increase in benthic denitrification could not compensate for the much larger increase in stream NO3- fluxes during high flow. Consequently, fractional NO3- losses were relatively low during high flow. 相似文献