An aerobic sequencing batch reactor for 2,4,6-trinitrophenol (picric acid) biodegradation

A bench scale sequencing batch reactor (SBR) was designed and tested for degradation of 2,4,6-trinitrophenol (TNP) or picric acid-contaminated wastewater or groundwater. Under varying temperatures (25, 15 and 10 degrees C) and influent concentrations (40-200 mg/L TNP) a stable biomass was developed that was consistently capable of degrading the explosive compound to below regulatory drinking water limits (0.057 mg/L). The reactor was initially seeded with a nitroaromatic and nitramine degrading isolate Rhodococcus opacus strain JW01. Kinetic growth modeling was conducted revealing micro(max) values at 25, 15 and 10 degrees C of 0.14, 0.08 and 0.04 d(-1), while the modeled K(s) values were 0.68, 1.11 and 1.24 mg/L, respectively. Overall TNP removal efficiency in the SBR was on average > 99.9% over the 2000 hours of operation. Removal of TNP to below drinking water standards, with low residual dissolved carbon and significant release of nitrogen from the parent compound was accomplished.     

Nitrite elimination and hydrolytic ring cleavage in 2,4,6-trinitrophenol (picric acid) degradation

Two hydrogenation reactions in the initial steps of degradation of 2,4,6-trinitrophenol produce the dihydride Meisenheimer complex of 2,4,6-trinitrophenol. The npdH gene (contained in the npd gene cluster of the 2,4,6-trinitrophenol-degrading strain Rhodococcus opacus HL PM-1) was shown here to encode a tautomerase, catalyzing a proton shift between the aci-nitro and the nitro forms of the dihydride Meisenheimer complex of 2,4,6-trinitrophenol. An enzyme (which eliminated nitrite from the aci-nitro form but not the nitro form of the dihydride complex of 2,4,6-trinitrophenol) was purified from the 2,4,6-trinitrophenol-degrading strain Nocardioides simplex FJ2-1A. The product of nitrite release was the hydride Meisenheimer complex of 2,4-dinitrophenol, which was hydrogenated to the dihydride Meisenheimer complex of 2,4-dinitrophenol by the hydride transferase I and the NADPH-dependent F(420) reductase from strain HL PM-1. At pH 7.5, the dihydride complex of 2,4-dinitrophenol is protonated to 2,4-dinitrocyclohexanone. A hydrolase was purified from strain FJ2-1A and shown to cleave 2,4-dinitrocyclohexanone hydrolytically to 4,6-dinitrohexanoate.     

Biodegradation of 2,4,6-trinitrophenol (picric acid) in a biological aerated filter (BAF)

This study demonstrated the microbial purification of a model wastewater containing 2,4,6-trinitrophenol (TNP), which was carried out in a continuously working biological aerated filter (BAF). The main emphasis was on the operating performance of the reactor as a function of the pollution load. TNP was degraded at a maximum volumetric removal rate of 2.53 g TNP/L d, with low residual COD and TNP concentration. Overloading of TNP inhibited the nitrite-oxidizing activity, resulting in poor TNP degradation performance in the BAF system. The inhibition depended on some factors, such as influent concentrations and flow rates of the influent. It is assumed that nitrite-oxidizing occurred spontaneously during TNP degradation in the BAF system, could have significant influence on TNP wastewater treatment. One year after the reactor start-up, the dominance of Rhodococcus, which was initially inoculated in the reactor, was confirmed by analysis of 16S rDNA sequence of the PCR products separated by DGGE.     

Converging catabolism of 2,4,6-trinitrophenol (picric acid) and 2,4-dinitrophenol by Nocardioides simplex FJ2-1A

Initial F₄₂₀-dependent hydrogenation of 2,4,6-trinitrophenol(picric acid) generated the hydride -complex of picrate and finally the dihydride complex.With 2,4-dinitrophenol the hydride -complex of 2,4-dinitrophenolis generated. The hydride transferring enzyme system showed activity against several substituted2,4-dinitrophenols but not with mononitrophenols. A K_m-value of0.06 mM of the hydride transfer for picrate as substrate was found. The pH optimaof the NADPH-dependent F₄₂₀ reductase and for the hydride transferase were 5.5and 7.5, respectively. An enzymatic activity has been identified catalyzing the releaseof stoichometric amounts of 1 mol nitrite from 1 mol of the dihydride -complexof picrate. This complex was synthesized by chemical reduction of picrate and characterizedby ¹H and ¹³C NMR spectroscopy. The hydride -complex of 2,4-dinitrophenolhas been identified as the denitration product. The nitrite-eliminating activitywas enriched and clearly separated from the hydride transferring enzyme system byFPLC. 2,4-Dinitrophenol has been disproven as a metabolite of picrate (Ebert et al. 1999)and a convergent catabolic pathway for picrate and 2,4-dinitrophenol with thehydride -complex of 2,4-dinitrophenol as the common intermediate has been demonstrated.     

Mineralization of pentachlorophenol with enhanced degradation and power generation from air cathode microbial fuel cells

The combined anaerobic-aerobic conditions in air-cathode single-chamber MFCs were used to completely mineralize pentachlorophenol (PCP; 5 mg/L), in the presence of acetate or glucose. Degradation rates of 0.140 ± 0.011 mg/L-h (acetate) and 0.117 ± 0.009 mg/L-h (glucose) were obtained with maximum power densities of 7.7 ± 1.1 W/m(3) (264 ± 39 W/m(2), acetate) and 5.1 ± 0.1 W/m(3) (175 ± 5 W/m(2), glucose). At a higher PCP concentration of 15 mg/L, PCP degradation rates increased to 0.171 ± 0.01 mg/L-h (acetate) and 0.159 ± 0.011 mg/L-h (glucose). However, power was inversely proportional to initial PCP concentration, with decreases of 0.255 W/mg PCP (acetate) and 0.184 W/mg PCP (glucose). High pH (9.0, acetate; 8.0, glucose) was beneficial to exoelectrogenic activities and power generation, whereas an acidic pH = 5.0 decreased power but increased PCP degradation rates (0.195 ± 0.002 mg/L-h, acetate; 0.173 ± 0.005 mg/L-h, glucose). Increasing temperature from 22 to 35°C enhanced power production by 37% (glucose) to 70% (acetate), and PCP degradation rates (0.188 ± 0.01 mg/L-h, acetate; 0.172 ± 0.009 mg/L-h, glucose). Dominant exoelectrogens of Pseudomonas (acetate) and Klebsiella (glucose) were identified in the biofilms. These results demonstrate that PCP degradation using air-cathode single-chamber MFCs may be a promising process for remediation of water contaminated with PCP as well as for power generation.     

降解水稻秸秆的复合菌系及其微生物群落结构演替北大核心CSCD

【目的】比较和分析从堆肥中富集的水稻秸秆降解菌系F1和F2的纤维素分解能力、微生物群落结构及其在秸秆降解过程中的演替,从而探究微生物群落结构与秸秆降解效率的相关性。【方法】采用DNS(3,5-二硝基水杨酸,3,5-dinitrosalicylic acid)定糖法测定发酵液中的外切纤维素酶活;采用范氏(Van Soest)洗涤纤维分析法测定发酵前与发酵后的秸秆纤维素、半纤维素、木质素的含量,并计算降解率;采用16S r RNA基因序列分析和实时荧光定量PCR(Quantitative real-time PCR,Q-PCR)对秸秆降解过程中的微生物物种组成及特定的功能微生物进行定性和定量分析。【结果】复合菌系F1的水稻秸秆总降解率、纤维素降解率、半纤维素降解率显著高于复合菌系F2;2种复合菌系的外切纤维素酶活性与cel48基因的拷贝数变化趋势一致;复合菌系F1的物种较丰富,优势物种是好氧细菌,复合菌系F2的物种组成较单一,培养后期具有较高比例的厌氧纤维素分解菌;培养前4天,复合菌系F1和F2的优势物种均为Unclassified Bacillales和Bacillus;第4天之后,不同复合菌系的优势物种及丰度出现差异,F1的优势物种主要属于Bacteroidetes,F2的优势物种主要属于Firmicutes;虽然Petrimonas和Pusillimonas是培养后期的共有优势物种,但是Petrimonas在复合菌系F2中的相对丰度(38.30%)显著高于F1(9.47%),且培养第8天的F2中的Clostridiales OPB54增加至14.85%。【结论】cel48基因拷贝数变化与秸秆纤维素的降解效率、外切纤维素酶活性变化具有一定的相关性,cel48基因可作为潜在的生物分子标记监测秸秆纤维素的降解过程;微生物群落结构对秸秆纤维素的降解效率具有显著影响,Unclassified Bacillales,Bacillus,Petrimonas,Pusillimonas是复合菌系F1和F2降解秸秆纤维素过程中的重要物种。     

Mineralization Potential of Atrazine and Degradation Intermediates from Clustered Characteristics in Inoculated Soils

Soil properties impact pesticide persistence. Because these characteristics operate together in situ, identification of their clustered associations can help explain pesticide fate. Factor analysis was used to reduce the dimensionality of soil characteristics by grouping them into clustered independent factors, which were then related to the mineralization of atrazine and selected degradation intermediates. A Sharpsburg silty clay loam, Ortello sandy loam, and Hord silt loam were inoculated with a Hord soil that had a high capacity for atrazine mineralization. The soils were spiked with ¹⁴C-radiolabeled atrazine, deethylatrazine, hydroxyatrazine, N-isopropylammeline, N-isopropylammelide or cyanuric acid and sampled during incubation for 80 d (atrazine) or 40 d (degradation intermediates) at 22°C. Low mineralization in uninoculated soils demonstrated that the absence of atrazine-mineralizing microorganisms was most limiting. In inoculated soils, regression analysis indicated mineralization of atrazine (R² = 0.88) and its degradation intermediates (R² ≥ 0.89) was related to factors associated with bioavailability and microbial activity. For atrazine, this relationship indicated mineralization may be positively influenced by higher pH and available phosphorus, lower NO₃-N, organic carbon and clay contents, and lower adsorption. Our results show how factor analysis can be used in conjunction with multiple regression to determine mineralization potential and thus help identify soils with limited degradation capacities and possible long-term persistence.     

Formation of hydride-Meisenheimer complexes of picric acid (2,4, 6-trinitrophenol) and 2,4-dinitrophenol during mineralization of picric acid by Nocardioides sp. strain CB 22-2

There are only a few examples of microbial conversion of picric acid (2,4,6-trinitrophenol). None of the organisms that have been described previously is able to use this compound as a sole source of carbon, nitrogen, and energy at high rates. In this study we isolated and characterized a strain, strain CB 22-2, that was able to use picric acid as a sole source of carbon and energy at concentrations up to 40 mM and at rates of 1.6 mmol. h(-1). g (dry weight) of cells(-1) in continuous cultures and 920 micromol. h(-1). g (dry weight) of cells(-1) in flasks. In addition, this strain was able to use picric acid as a sole source of nitrogen at comparable rates in a nitrogen-free medium. Biochemical characterization and 16S ribosomal DNA analysis revealed that strain CB 22-2 is a Nocardioides sp. strain. High-pressure liquid chromatography and UV-visible light data, the low residual chemical oxygen demand, and the stoichiometric release of 2.9 +/- 0.1 mol of nitrite per mol of picric acid provided strong evidence that complete mineralization of picric acid occurred. During transformation, the metabolites detected in the culture supernatant were the [H-]-Meisenheimer complexes of picric acid and 2,4-dinitrophenol (H--DNP), as well as 2,4-dinitrophenol. Experiments performed with crude extracts revealed that H--DNP formation indeed is a physiologically relevant step in picric acid metabolism.     

A highly sensitive and selective detection of picric acid using fluorescent sulfur‐doped graphene quantum dots

The development of an analytical probe to monitor highly mutagenic picric acid (PA) carries enormous significance for the environment and for health. A novel, simple and rapid fluorescence analytical assay using sulfur‐doped graphene quantum dots (SGQDs) was designed for the highly sensitive and selective detection of PA. SGQDs were synthesized via simple pyrolysis of 3‐mercaptopropionic acid and citric acid and characterized using advanced analytical techniques. Fluorescence intensity (FI) of SGQDs was markedly quenched by addition of PA, attributed to the inner filter effect and dominating static quenching mechanism between the two, in addition to a significant colour change. The calibration curve of the proposed assay exhibited a favourable linearity between quenched FI and PA concentration over the 0.1–100 μΜ range with a lowest detection limit of 0.093 μΜ and a correlation coefficient of 0.9967. The analytical assay was investigated for detection of trace amounts of PA in pond and rain water samples and showed great potential for practical applications with both acceptable recovery (98.0–100.8%) and relative standard deviation (1.24–4.67%). Analytical performance of the assay in terms of its detection limit, linearity range, and recovery exhibited reasonable superiority over previously reported methods, thereby holding enormous promise as a simple, sensitive, and selective method for detection of PA.     

秸秆降解菌的筛选及对秸秆的降解效果

作物秸秆作处置不当可能严重影响农村生态环境。目前东北地区的秸秆处置方式主要为直接打碎还田,但秸秆在自然环境中不易腐化,影响春耕。从添加外源微生物促进秸秆原位腐化角度开发新型可培养秸秆降解菌,具有重要意义。本实验通过菌种富集培养、刚果红培养基初筛和滤纸条崩解试验复筛的方法,从腐烂的秸秆和牛肠道中分离筛选潜在的高效纤维素降解菌,测定其最适生长温度和pH,在液态发酵培养条件下考察菌株实际降解能力,共获得具有较高玉米秸秆降解能力的降解菌5株。5种菌株的生长峰值均出现在温度20～30℃,pH值7.5～8.5范围内。液态发酵培养15天后,秸秆失重率为菌株NX9(53.88%)>NF6(51.36%)>JF3(46.97%)>JZ8(45.2%)>JX4(35.79%)>CK(23.88%)。其中,菌株NX9(温度30℃、pH 7.5)对秸秆半纤维素和木质素的降解能力最强,15天降解率分别为48%和37.7%;筛选出的NF6和JF3属于耐冷微生物,特别是菌株NF6在4℃条件下也能生长繁殖,为北方开展"外源微生物促进秸秆原位腐化"技术提供了基础。     

Biodegradation of 2,4,6-trinitrotoluene (TNT): An enzymatic perspective

Enzymatic degradation of TNT by aerobic bacteria is mediated by oxygen insensitive (Type 1) or by oxygen sensitive nitroreductases (Type II nitroreductases). Transformation by Type I nitroreductases proceeds through two successive electron reductions either by hydride addition to the aromatic ring or by direct nitro group reduction following a ping pong kinetic mechanism. TNT is reduced to the level of hydroxylaminodinitrotoluenes and aminodinitrotoluenes by pure enzyme preparations without achieving mineralization. Interestingly, database gene and amino acid sequence comparisons of nitroreductases reveal a close relationship among all enzymes involved in TNT transformation. They are all flavoproteins which use NADPH/NADH as electron donor and reduce a wide range of electrophilic xenobiotics. TNT degradation by fungi is initiated by mycelia bound nitroreductases which reduce TNT to hydroxylaminodinitrotoluenes and aminodinitrotoluenes. Further degradation of these products and mineralization is achieved through the activity of oxidative enzymes especially lignin degrading enzymes (lignin and manganese peroxidases).     

磷脂脂肪酸分析方法在微生物生态学中的应用

磷脂脂肪酸分析方法(PLFA)是基于生物化学手段的一种微生物生态学研究新技术,它具有对细胞生理活性没有特殊的要求,对样品保存时间也要求不高等优点,由样品中所有微生物提供信息,是一种快捷、可靠的分析方法。本文介绍了PLFA在微生物生态学研究中的应用,主要包括对微生物群落生物量、群落结构和功能及其变化,指示特定微生物以及营养状况方面的研究。     

聚苹果酸的微生物合成及应用研究进展

聚苹果酸是一种优良的完全可生物降解的生物活性材料,在医学和药学领域有着极大的应用潜力。文中结合我们的工作总结了近年来聚苹果酸代谢、聚苹果酸的微生物发酵合成以及聚苹果酸在医药领域的应用等方面的研究进展,并对聚苹果酸的深入研究作了展望。     

土壤微生物群落磷脂脂肪酸PLFA生物标记多样性

磷脂脂肪酸(PLFA)生物标记法是一种可定性和定量分析土壤中微生物群落多样性的方法.研究以烟田土壤为例,应用生态学评价方法,即丰富度 (S)、均匀度(J)、Simpson优势度(D)、Shannon-Wiener(H1)、Brillouin(H2)和McIntosh(H3)多样性指数等测度方法,分析土壤中微生物群落PLFAs生物标记的多样性.研究结果表明,供试土壤微生物群落中,先后出现了43种PLFAs,将其聚类分析,可以将所获得的PLFAs分成五大类:第Ⅰ类为高含量、高频次和多样性,PLFA为18:1ω9c的真菌生物标记;第Ⅱ类为高含量、高频次和多样性,PLFA为16:0的假单胞菌生物标记;第Ⅲ类为高含量、高频次,多样性中等,PLFA为16:1ω5c的甲烷氧化菌生物标记;第Ⅳ类为中等含量,频次较高,多样性中等,含有表征好氧菌的i15:0、a15:0、i16:0和a17:0的PLFA,还有表征厌氧菌的18:1ω7c以及硫酸盐还原菌的16:0 10Me;第Ⅴ类为低含量,低频次和多样性,其特征生物标记有表征好氧菌的I 15:0 3OH、15:1 I G、a16:0、i16:1 G、i16:1 H、17:0、i17:0、15:0 2OH、15:0 3OH、17:0和17:0 2OH的PLFAs,存在有表征真菌的18:3ω6c (6,9,12)、放线菌的17:0 10Me和18:0 10Me以及表征原生动物的20:4ω6,9,12,15c.说明供试土壤中能够起主导作用的功能菌依次是真菌、假单胞菌、甲烷氧化菌和部分的好氧菌、厌氧菌及硫酸盐还原菌,将为合理调节土壤微生态系统提供指导,是一种可行的评价土壤微生物群落多样性的新方法.     

耐盐碱微生物菌种的筛选鉴定及其功能性与促生性

【背景】近年来,甘肃省土地盐碱化的日益加剧已对当地农业生产和生态环境产生严重影响。【目的】从甘肃省兰州市兰州新区和张掖市黑河生态保护区盐碱土壤中分离筛选出耐盐碱菌株,并对其进行鉴定和部分功能性评价与促生性分析,从而为改良甘肃省盐碱地提供微生物资源和理论基础。【方法】利用不同盐碱浓度的改良培养基对分离后的菌落进行条件培养,筛选出具有高耐盐碱能力的菌种,通过16S rRNA基因序列鉴定菌种类型,并测试其在不同培养基条件下功能性和促生性的不同作用。【结果】共筛选得到5株高耐盐碱菌株,鉴定结果分别为巨大芽孢杆菌（Bacillus megaterium）、金黄节杆菌（Arthrobacter aurescens）、费氏中华根瘤菌（Sinorhizobium fredii）、地衣芽孢杆菌（Bacillus licheniformis）和不动杆菌属（Acinetobacter sp.）。经鉴定分析5株菌均具有溶磷和分泌吲哚乙酸的能力;金黄节杆菌和地衣芽孢杆菌具有解钾能力;金黄节杆菌、费氏中华根瘤菌和不动杆菌属具有固氮能力;地衣芽孢杆菌、巨大芽孢杆菌和费氏中华根瘤菌分泌的ACC脱氨酶活性分别达到0.272、0.217和0.159 U/mg,金黄节杆菌和不动杆菌属几乎无ACC脱氨酶活性。【结论】五株耐盐碱菌在溶磷、解钾和固氮功能方面各自具有不同的效果且兼具一定的促生作用,这为后期微生物改良盐碱地的应用提供了物种资源和理论基础。     

Empirical modeling of batch fermentation kinetics for poly(glutamic acid) production and other microbial biopolymers

An empirical kinetic model is proposed for the batch production of poly(glutamic acid) from Bacillus subtilis IFO 3335. In addition, the proposed model was used to fit the kinetic data of poly(glutamic acid) production from other bacterial strains using different media, as well as kinetic data from different strains for the production of the exocellular biopolymers dextran, hyaluronic acid, xanthan, alginate, and the endocellular biopolymer polyhydroxybutyrate. The empirical model treats the biopolymer as a component of the biomass and fits the experimental biomass data using a sigmoidal relationship that includes the maximum specific growth rate, mu(max), and the substrate saturation parameter, K(S). An empirical parameter, the relative coefficient (r), quantifies, in relative terms, the degree of nongrowth-associated biopolymer formation.     

不同放牧与围封高寒灌丛草地土壤微生物群落结构PLFA分析

土壤微生物群落可以指示土壤质量变化,是土壤生态系统变化的预警及敏感指标。采用磷脂脂肪酸(PLFA)分析方法研究了高寒杜鹃灌丛草地不同强度放牧及围封后,土壤微生物群落结构特征的变化规律和响应。结果显示,高寒杜鹃灌丛草地土壤总PLFA量、细菌生物量、真菌生物量和放线菌生物量均随着放牧强度的增大而显著降低(P0.05)。重牧灌丛草地,围封后的土壤总PLFA量、细菌生物量、放线菌生物量、G~+/G~-和压力指数显著高于放牧处理,而细菌/真菌比显著低于放牧处理;中牧灌丛草地,围封后的土壤总PLFA量、细菌生物量、细菌/真菌比显著高于放牧处理,而真菌生物量和压力指数显著低于放牧处理;轻牧灌丛草地,围封处理的土壤各生物量和生物量比值与放牧处理无显著差异。PLFA主成分分析表明:主成分一(PC1)主要包括14:0、15:0、10Me16:0和18:1ω9c等直链饱和脂肪酸和单不饱和脂肪酸,占PC1的53.68%;主成分二(PC2)主要包括由i16:0、16:1ω7c、i17:0、cy17:0、17:0、18:1ω9t、18:0和cy19:0等支链饱和脂肪酸和环丙烷脂肪酸组成,占PC2的51.34%;各处理样地土壤微生物群落结构相似;围封处理的响应程度大于放牧处理。相关性分析表明,土壤总PLFA量、细菌生物量、真菌生物量和放线菌生物量与土壤有机碳、全氮均呈极显著正相关,细菌/真菌比值与土壤有机碳、全氮呈极显著负相关。以上表明过度放牧降低了高寒灌丛草地土壤微生物活性,显著降低了土壤微生物生物量,适度放牧和围封可维持土壤微生物群落结构的稳定,围封有利于过度放牧草地土壤微生物的恢复。     

Fatty acid methyl ester (FAME) profiles as measures of soil microbial community structure

Analysis of fatty acid methyl ester (FAME) profiles extracted from soils is a rapid and inexpensive procedure that holds great promise in describing soil microbial community structure without traditional reliance on selective culturing, which seems to severely underestimate community diversity. Interpretation of FAME profiles from environmental samples can be difficult because many fatty acids are common to different microorganisms and many fatty acids are extracted from each soil sample. We used principal components (PCA) and cluster analyses to identify similarities and differences among soil microbial communities described using FAME profiles. We also used PCA to identify particular FAMEs that characterized soil sample clusters. Fatty acids that are found only or primarily in particular microbial taxa-marker fatty acids-were used in conjunction with these analyses. We found that the majority of 162 soil samples taken from a conventionally-tilled corn field had similar FAME profiles but that about 20% of samples seemed to have relatively low, and that about 10% had relatively high, bacterial:fungal ratios. Using semivariance analysis we identified 21:0 iso as a new marker fatty acid. Concurrent use of geostatistical and FAME analyses may be a powerful means of revealing other potential marker FAMEs. When microbial communities from the same samples were cultured on R2A agar and their FAME profiles analyzed, there were many differences between FAME profiles of soil and plated communities, indicating that profiles of FAMEs extracted from soil reveal portions of the microbial community not culturable on R2A. When subjected to PCA, however, a small number of plated communities were found to be distinct due to some of the same profile characteristics (high in 12:0 iso, 15:0 and 17:1 ante A) that identified soil community FAME profiles as distinct. Semivariance analysis indicated that spatial distributions of soil microbial populations are maintained in a portion of the microbial community that is selected on laboratory media. These similarities between whole soil and plated community FAME profiles suggest that plated communities are not solely the result of selection by the growth medium, but reflect the distribution, in situ, of the dominant, culturable soil microbial populations.     

Structured modeling of a microbial system: I. A theoretical study of lactic acid fermentation

Most fermentation models presented in the literature are unstructured, i.e., the biomass composition is assumed constant during all operating conditions. These models are unable to simulate experiments carried out at widely different operating conditions. It is therefore interesting to examine simple structured models where knowledge of the cell physiology is taken into account in the modeling phase. In this article, a simple structured model is presented. The model is based on experimental work with the lactic acid bacteria Streptococcus cremoris, but due to the similarities in basic metabolism for many microorganisms it is applicable also for other fermentation system. The basic assumption in the model is that the biomass can be divided into two parts (compartments)-an active part and a mainly inactive structural part. The size of the active part has a pivotal role in the model.