pattern of cultured human methanogens

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《跨文化交际》课程教学大纲

《跨文化交际》课程教学大纲

《跨文化交际》课程教学大纲课程编号:ENGL2046课程类别:专业选修课程授课对象:英语专业、俄英双语、法英双语学生开课学期:英语第6学期、双语第8学期学分:2 学分主讲教师:指定教材:《跨文化交流入门》,浙江大学出版社,许力生主编,2004年。

《文化与交际》,暨南大学出版社,胡穗鄂编。

教学目的:目前我国经济快速增长,文化交流、旅游业蓬勃发展。

江、浙、沪地区外国独资、合资企业数量增多,与国际人员的经济文化交往日益增多。

跨文化交际现象已经成为苏州本地文化的一个重要方面。

但是,在众多的跨文化交际中,一些人员出现文化误解,或者表现出不自信,降低了交际的效益,直接的后果往往导致经济效益的降低。

苏州大学作为本地的人才高地,有责任、有条件在教学中培养学生的跨文化交际能力。

我们的毕业生主要从事文化、教育、经济活动,我们的课程也应适应这社会需要,帮助学生通过知识的获取、情感的开放和技能的培养形成以自我文化又和他国文化保持一定距离的跨文化意识,也就是说一种能以局外者的眼光看待自己文化的能力;局内者的眼光理解自己和他人的文化意识;培养学生在交际中对他国文化和本土文化怀有好奇、开放和宽容的态度。

从而在国际交往中提高交际的效益,提升个人的自信心。

本课程采用课堂教学、学期作业和网络平台相结合的教学形式。

课堂教学采用多种教学法综合进行教学。

课堂语言为英语。

采用理论与实践活动相结合的方式,与学生互动探讨理论。

参插角色扮演、小组讨论、全班讨论的活动方式,进行情景模拟实验、引导学生发表观点。

另外有录音、录像供学生观摩讨论。

学期作业的形式是一篇千字以上的论文,内容是运用学到的某些跨文化交际的理论概念对现实生活案例、本土文化和外国文化进行阐释、分析、比较和反思。

学生必须自己选题、规划。

文章材料包括文字、图片、音频和视频,教师的工作是建议、修改、监督和评估,创造机会,帮助学生完成学期论文。

该课程有两个网站:一个是在外国语学院服务器上的课程资源网站,网站上有该课程的教学大纲、进度表、备课教案,另设有通知板、网上跨文化交际咖啡俱乐部、学习工具等帮助学生完成科目的服务性网站。

cultural patterns 文化模式

cultural patterns 文化模式

cultural patterns 文化模式"Cultural Patterns: An Exploration of Their Origin, Influence, and Impact"IntroductionCultural patterns refer to the shared beliefs, customs, habits, values, and behaviors that are characteristic of a particular group of people, society, or community. These patterns shape the way individuals perceive, think, and act, and help establish a sense of identity and belonging. In this article, we will delve into the origin, influence, and impact of cultural patterns, exploring how they are developed and perpetuated and how they shape our lives.Origin of Cultural PatternsCultural patterns are not static entities; they evolve and develop over time through various processes. The origin of cultural patterns can be traced back to the early experiences and interactions of a community. These experiences often include factors such as geographic location, historical events, and socio-political aspects. For example, the traditional dress, cuisine, and rituals of acommunity may be influenced by the local climate, historical events such as colonization or cultural exchange, and social hierarchies.Influence of Cultural PatternsCultural patterns have a significant influence on individuals, societies, and even global dynamics. They shape our thoughts, perspectives, and behaviors and determine how we interact with others. Cultural patterns influence language, communication styles, social norms, and values, as well as attitudes towards education, work, and relationships.Language, for instance, is a fundamental cultural pattern that influences the way we express ourselves and understand the world. Different languages have unique structures, vocabularies, and expressions, and shape the way individuals think and communicate. The importance placed on education and the role of family can also vary significantly across cultures, with some emphasizing collective harmony and respect for authority, while others encourage individualism and critical thinking.Impact of Cultural PatternsThe impact of cultural patterns can be seen in various domains of life, from social interactions to economic systems. Social customs and traditions play a vital role in maintaining social cohesion and creating a sense of identity within a community. For example, cultural rituals and celebrations foster a collective sense of belonging and represent the values and beliefs of a society. They provide an opportunity to transmit cultural knowledge and promote intergenerational bonds.Cultural patterns also influence economic systems and consumer behaviors. For instance, in some cultures, individuals prioritize saving money or investing in real estate, while in others, they may value experiences and spending on travel and entertainment. These cultural attitudes towards money and consumption shape economic trends and impact industries such as tourism and luxury goods.Importantly, cultural patterns also contribute to social inequalities and power dynamics. Gender roles and expectations, social hierarchies, and discrimination are often perpetuated throughcultural patterns. For example, traditional gender roles may limit opportunities for women in certain societies, while racial biases may be reinforced through cultural norms and values. Recognizing and challenging these patterns is crucial for promoting social justice and equality.ConclusionCultural patterns are the fabric that holds societies together and shapes our individual experiences. They are born out of historical, physical, and socio-political factors, and influence our thoughts, behaviors, and interactions. From language and social customs to economic systems and power dynamics, cultural patterns have a profound impact on our daily lives. In embracing and understanding cultural patterns, we can appreciate diversity, foster empathy and respect, and work towards a more equitable and inclusive world.。

生物医用材料

生物医用材料
Review /CR
Biomimetic Cell Culture Proteins as Extracellular Matrices for Stem Cell Differentiation
Akon Higuchi,*,†,‡,§ Qing-Dong Ling,§,∥ Shih-Tien Hsu,⊥ and Akihiro Umezawa‡
© 2012 American Chemical Society
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CONTENTS
1. Introduction 2. Cell Sources and Analysis of Differentiation Lineages of MSCs 2.1. Cell Sources 2.2. Analysis of Differentiation Lineages 3. Preparation of Culture Matrix 3.1. ECM Immobilization on 2D Dishes 3.2. 3D Culture in Hydrogels 3.2.1. Photocross-Linking of ECM Proteins and ECM Peptides 3.2.2. Chemical Cross-Linking of Hydrogels 3.3. 3D Culture in Scaffolds 3.3.1. Preparation of Scaffolds 3.4. 3D Culture in Nanofibers 4. Physical Properties of Biopolymers (Biomaterials) Guide Stem Cell Differentiation Fate (Lineage) 4.1. Mechanical Stretching Effect of Culture Surface-Coated with ECM Proteins 4.2. Low Oxygen Expansion Promotes Differentiation of MSCs 4.3. Other Physical Effect Affecting Differentiation of MSCs 5. MSC Culture on ECM Proteins and Natural Biopolymers 5.1. Chemical and Biological Interactions of ECM Proteins and Stem Cells 5.2. Collagen 5.2.1. Collagen Type I Scaffolds 5.2.2. Organic Hybrid Scaffolds of Collagen Type I 5.2.3. Scaffolds Using Collagen Type II and Type III

Cultural Patterns

Cultural Patterns

Definitions of Cultural Patterns
People and cultures are extremely complex and consist of numerous interrelated cultural orietation. A useful umbrella term that allows us to talk about beliefs and values and other orientations collectively is cultural patterns. We should think of cultural patterns as a system of beliefs and values that work in combination to provide a coherent, if not always consistent, model for perceiving the world.
Beliefs

According to Rogers and Steinfatt, "Beliefs serves as the storage system for the content of our past experiences, including thoughts, memories, and interpretations of events. Beliefs are shaped by the individual's culture."
Perception and Culture: perception is culturally
determined. We learn to see the world in a certain way based on our cultural background. These two concepts, working in combination, form what we called cultural patterns.

大学英语跨文化交际chapter 1 Culture

大学英语跨文化交际chapter 1 Culture

DEFINITIONS OF ‘CULTURE’
1. Defining Culture from the Anthropological Perspective 2. Defining Culture from the Psychological Perspective 3. Defining Culture from the Sociological Perspective 4. Defining Culture from the Intercultural Perspective 5. Our Definition of Culture
3. Culture Is Like the Water a Fish Swims In
3. Culture Is Like the Water a Fish Swims In Human cannot live without culture. Culture is what the world is like for us. We take for granted the culture whe 1 Culture
Chapter Outline
The nature of culture The definition of culture The characteristics of culture Cultural identity Cultures within culture
Text A: The Nature of Culture
Think about the following similes and metaphors, how do you think culture is related to the references? 1. Culture is like an iceberg. 2. Culture is our software. 3. Culture is like the water a fish swims in. 4. Culture is the grammar of our behavior.

跨文化交际

跨文化交际

Human Nature Orientation人的本性取向
1 Cultures that begin with the premise that people are instrinsically evil and therefore cannot be trusted seek to control the actions of their members with institutions ranging from the religious to the political.
--His most notable work has been in developing cultural dimensions theory. The four dimensions are; Power Distance, Individualism-Collectivism, Uncertainty and Avoidance( 不确定性 - 规避性), Masculinity and Femini 1
蔡兴艳
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2.The middle or so-called cooperation view is widesread and is associated with Asians and Native Americans. This orientation affirms that people should, in every way possible, live in harmony with nature. The philosophy holds that a "power" links all things and creatures together.
※Masculinity and femininity男性化/女性化 Masculinity is the extent to which the dominant values in a society are male oriented and is associated with such behaviors as ambition, differentiated sex roles, achievement, the aquisition of money, and signs of maniness. “男性化”倾向社会中两 性的社会性别角色差别清 楚,男人应表现得自信、 坚强、注重物质成就,女 人应表现得谦逊、温柔、 关注生活质量。

产甲烷杆菌的研究和其利用前景

产甲烷杆菌的研究和其利用前景

《微生物学》课程论文论文题目:产甲烷杆菌的研究和其利用前景工艺学学院:生命与地理科学学院专业:生物科学班级:S10A学号:20101911131姓名:刘韬成绩:目录1 产甲烷菌的分类................................................................................................................................ -2 -2.产甲烷菌的生态多样性.................................................................................................................... - 2 - 3.生长繁殖特别缓慢.......................................................................................................................... - 3 -4.产甲烷菌代谢途径............................................................................................................................ - 3 -5.甲烷合成的途径................................................................................................................................ - 3 -6.沼气池中产甲烷杆菌和不产甲烷菌的关系.................................................................................... - 4 -6.1不产甲烷细菌为产甲烷菌提供生长基质和产甲烷所需的底物 ......................................... - 4 -6.2不产甲烷细菌为产甲烷菌创造适宜的厌氧环境................................................................. - 4 -6.3不产甲烷细菌为产甲烷菌清除有毒物质............................................................................. - 4 -6.4产甲烷菌为不产甲烷细菌生化反应解除反馈抑制............................................................. - 4 -6.5共同维持沼气发酵环境中的适宜pH值............................................................................... - 5 -6.6不产甲烷细菌构建了产甲烷菌的“古环境” ....................................................................... - 5 -7.产甲烷杆菌的应用前景.................................................................................................................... - 5 -7.1废水处理................................................................................................................................. - 5 -7.2酿酒工业上的应用................................................................................................................. - 5 -7.3产甲烷菌在煤层气开发中的应用......................................................................................... - 6 -8. 结语................................................................................................................................................ - 6 - 参考文献................................................................................................................................................ - 6 -产甲烷杆菌的研究和其利用前景10级生物科学 20101911131 刘韬摘要产甲烷菌是一类重要的极端环境微生物,在地球生物化学碳素循环过程中起着关键作用. 目前,根据产甲烷菌的系统发育和生理生化特性可将已培养的产甲烷菌分为5大目. 产甲烷菌广泛分布在海底及淡水沉积物、水稻田、动物胃肠道、地热及地矿等环境中,生态学研究表明,产甲烷菌在不同的生态环境里具有不同的群落分布特点,并且受不同环境因子的影响而显示出不同的生理代谢功能. 本文综述了国内外近年来产甲烷菌的分类及生态多样性研究进展,同时简述了产甲烷菌在厌氧生物处理和工业酿酒中广阔应用前景.关键词产甲烷菌;分类;生态多样性;废水处理;泸州老窖Methanobacterium research and its prospect Abstract methanogens is an important kind of extreme environmental microbial, in the biogeochemistry of carbon cycle plays a key role in the process. At present, according to the methanogenic bacteria phylogeny and physiological and biochemical characteristics can be cultured methanogens have been divided into 5heads. Methane producing bacteria widely distributed in marine and freshwater sediments rice, water, animal gastrointestinal tract, geothermal and geological environment, ecological studies have indicated, methanogenic bacteria in different ecological environment has different characteristics of community distribution, and affected by different environmental factors and show different physiological and metabolic function. This article reviews the domestic and abroad in recent years and the classification of methane producingbacteria biodiversity research progress, at the same time on themethanogenic bacteria in anaerobic biological treatment and broadapplication prospects in industrial saccharomyces.Key words methanogens; classification; biodiversity; wastewatertreatment; Lu zhou产甲烷菌是一类严格厌氧的原核微生物,是有机物甲烷化作用中食物链的最后一组成员,其独特的厌氧代谢机制使其在自然界物质循环中起着重要作用. 一方面,产甲烷菌是产生温室气体的主要因素,全球甲烷的排放量每年大约是500 t,其中74%是由产甲烷菌代谢产生[1];另一方面,产甲烷菌在有机质的厌氧生物处理工业应用中发挥着关键的作用,如沼气发酵、煤层气开发等. 因此,对产甲烷菌的研究具有重要的理论和实践意义. 随着厌氧培养技术和微生物分子生态技术的发展,更多的实验室能对产甲烷菌进行多角度的研究. 这些研究揭示出产甲烷菌分类地位的多样性,展示出不同环境下产甲烷菌的生态及生理特性的差异性,同时也为产甲烷菌的实际工业应用指明了方向.1 产甲烷菌的分类1776年,Alessandro Volta首次发现了湖底的沉积物能产生甲烷,之后历经一个多世纪的研究,利用有机物产甲烷的厌氧微生物才大致被分为两类:一类是产氢、产乙酸菌,另一类就是产甲烷菌. W.E. Balch等在1979年报道了3个目、4个科、7个属和13个种的产甲烷微生物,他们的分类是建立在形态学、生理学等传统分类特征以及16S rRNA寡核苷酸序列等分子特征基础上的[2].随着厌氧培养技术和菌种鉴定技术的不断成熟,产甲烷菌的系统分类也在不断完善. 《伯杰系统细菌学手册》第9版将近年来的研究成果进行了总结和肯定,并建立了以系统发育为主的产甲烷菌最新分类系统. 产甲烷菌分可为5个大目,分别是:甲烷杆菌目(Methanobacteriales)、甲烷球菌目(Methanococcales)、甲烷微菌目(Methanomicrobiales)、甲烷八叠球菌目(Methanosarcinales)和甲烷火菌目(Methanopyrales) [3],上述5个目的产甲烷菌可继续分为10个科与31个属,它们的系统分类及主要代谢生理特性见表1.2.产甲烷菌的生态多样性产甲烷球菌发现于1982年,生活在260m深、200atm、94℃的海底火山口附近,属于原核生物中的古菌域,具有其它细菌如好氧菌、厌氧菌和兼性厌氧菌所不同的代谢特征. 产甲烷菌的甲烷生物合成途径主要是以乙酸、H2/CO2、甲基化合物为原料[4]. 产甲烷菌在自然界中分布极为广泛,在与氧气隔绝的环境几乎都有甲烷细菌生长,如海底沉积物、河湖淤泥、水稻田以及动物的消化道等. 在不同的生态环境下,产甲烷菌的群落组成有较大的差异性,并且其代谢方式也随着不同的微环境而体现出多样性.3.生长繁殖特别缓慢甲烷细菌生长很缓慢,在人工培养条件下需经过十几天甚至几十天才能长出菌落。

Cultural Patterns跨文化交际的文化模式知识分享

Cultural Patterns跨文化交际的文化模式知识分享

2. Obstacles In Studying Cultural Patterns
Cultural Patterns Are Often Contradictory.
– In many instances, we find contradictory values in a particular culture. That is, there is often a gulf between the values that are articulated and the values that are acted out.
Cultural Patterns Change.
– Cultures change and therefore so do the values of the culture.
– However, even granting the dynamic nature of culture and value systems, we again remind you that regardless of culture, the deep structures always resist change.
A useful umbrella term that allows us to talk about beliefs and values and other orientations collectively is cultural patterns.
1. Defining Cultural Patterns
2. Obstacles In Studying Cultural Patterns
Cultural Patterns Are Interrelated.

文化外译

文化外译

Defining Culture From an Intercultural Perspective
• American scholars Daniel Bates and Fred Plog: Culture is a system of shared beliefs, values, customs, behaviors, and artifacts that the members of a society use to cope with their world and with one another, and that are transmitted from generation to generation to generation through learning.
• Thank you
Defining Culture From an Sociological Perspective
• Social scientists: Culture is defined as a pattern of learned, group-related perception--including both verbal and attitudes, nonverbal language, attitudes, values, belief system, disbelief systems, and behavior.
• Defintio experience, beliefs, values, actions, attitudes, hierarchies, religions, notions of time, roles, spatial relations, concepts of the universe, and artifacts acquired by a group of people in the course of generations through individual and group striving.

人类学的四个基本问题

人类学的四个基本问题

人类学的四个基本问题Anthropology, as a field of study, is rooted in four fundamental questions that seek to understand the nature of human existence and culture: the biological, social, cultural, and linguistic aspects of being human. 人类学作为一门研究领域,根植于四个基本问题,旨在理解人类存在和文化的本质:生物学、社会、文化和语言方面的存在。

The biological aspect of anthropology examines the evolutionary history, genetics, and physical characteristics of human beings. From the study of fossil remains to the analysis of genetic markers, anthropologists seek to understand the origins and variations of the human species. 人类学的生物学方面研究人类的进化历史、遗传学和生理特征。

从化石遗骸的研究到遗传标记的分析,人类学家致力于理解人类物种的起源和变化。

From a social perspective, anthropology explores the ways in which humans organize themselves into societies, create social structures, and interact with one another. This includes the study of kinship systems, political organization, economic patterns, and social institutions. 从社会角度来看,人类学探讨人类如何组织成社会、创建社会结构并相互交往。

产甲烷菌的生态多样性及工业应用

产甲烷菌的生态多样性及工业应用
1 产甲烷菌的分类 1776年,Alessandro Volta首次发现了湖底的沉积物能产 生甲烷,之 后历 经 一 个 多世 纪 的 研 究,利 用 有 机 物产甲烷 的 厌氧微 生物才大 致被分为两类:一类是产氢、产乙酸菌,另 一类就是产甲烷菌. W.E. Balch等在1979年报道了3个目、4个 科、7个属和13个 种的产甲烷 微 生物,他们的 分 类 是 建 立在 形
2 产甲烷菌的生态多样性
产甲烷菌属于原核生物中的古菌域,具 有其它细菌如好
4期
傅 霖等:产甲烷菌的生态多样性及工业应用
575
分类单元(目) Taxon (Order)
甲烷杆菌目 Methanobacteriales
表1 产甲烷菌系统分类的主要类群及其生理特性[3] Table 1 Properties of major taxa of methanogens [3]
Abstract Methanogens are important extremophiles, which play a key role in the global carbon cycle. Recently, the cultured methanogens are grouped into five orders based on their phylogeny and phenotypic properties. In addition, there are many different habitats in nature for methanogens, such as marine and freshwater sediments, rice-field soils, animal gastrointestinal tracts, mineral and geothermal environment. The ecology of methanogens indicates that the different ecological methanogenic communities have different distribution characteristics, and the metabolic functions of methanogens are affected by different environmental factors. In this paper, the current knowledge methanogens, such as their definition in taxonomy and ecological diversity is reviewed, and some suggestions related to further studies on the application of methanogens in anaerobic biotreatment and biomethanization are provided. Tab 1, Ref 38 Keywords methanogen; classification; ecological diversity; anaerobic biotreatment; biogasification CLC Q939.908

Cultural-Patterns跨文化交际的文化模式PPT课件

Cultural-Patterns跨文化交际的文化模式PPT课件

3.2.1 High-Context
A high context (HC) communication or message is one in which most of the information is already in the person, while very little is in the coded, explicitly transmitted part of the message. In high-context cultures, people are very homogeneous with regard to experiences, information networks, and the like. High-context cultures, because of tradition and history, change very little over time.
3.1.3 Power Distance
The premise of the dimension deals with the extent to which a society accepts that power in relationships, institution, and organizations is distributed unequally. People in high-power-distance countries believe that power and authority are facts of life…Social hierarchy is prevalent and institutionalizes inequality. To people in low-power-distance countries, a hierarchy is an inequality of roles established for convenience.

patterns of culture书籍简介-概述说明以及解释

patterns of culture书籍简介-概述说明以及解释

patterns of culture书籍简介-概述说明以及解释1.引言1.1 概述《Patterns of Culture》是一本由美国人类学家Ruth Benedict所著的重要著作。

该书于1934年首次出版,以其深入而独特的研究视角,对人类文化进行了深入的探讨和研究。

本书通过对不同文化模式的分析和对比,以及对不同文化之间的联系和相互影响的研究,集中展示了人类文化的多样性和变异性。

《Patterns of Culture》以一个关键的观点为基础,即每个文化都是独特的,并且通过文化模式的传播和承继来表现出来。

这意味着文化并不是一成不变的,而是一个不断演变和适应的系统。

通过比较和分析不同文化中的模式和价值观念,本书揭示了不同文化之间的相似性和差异性,同时也展示了文化对个体行为和社会结构的影响。

在本书中,Ruth Benedict通过对三个不同文化的深入研究来展示她的观点。

她分别探讨了托特脱特尔人、祭司人和大草原人这三个文化群体,并描述了他们的文化模式、价值观念、社会结构以及对个体行为的影响。

通过具体案例的分析,读者可以更好地理解文化模式的形成和变化,并认识到文化对个体和群体的重要性。

总之,《Patterns of Culture》通过对不同文化之间的对比和分析,展示了人类文化的多样性和变异性。

本书为读者提供了一种全新的观察文化的角度和方法,激发了对文化多样性的深入思考,并为人们更好地理解和解释不同文化之间的相互联系和相互影响提供了重要的启示。

1.2文章结构文章结构是指文章按照一定的逻辑顺序组织和呈现内容的方式。

在本文中,文章的结构主要分为引言、正文和结论三个部分。

引言部分是文章的开头,旨在引起读者的兴趣并介绍文章的主题。

在引言部分,我们将概述本文的主要内容,即介绍《Patterns of Culture》一书的相关信息,并说明撰写此篇长文的目的。

正文部分是整篇文章的主体,用于详细阐述文化模式的定义和分类。

人面鱼纹盆的英语作文

人面鱼纹盆的英语作文

As a high school student with a keen interest in history and culture, I was thrilled when our class visited the local museum for a field trip. Among the myriad of artifacts, one piece stood out to me in particularthe humanfaced fish pattern basin. This ancient vessel, with its intricate design and profound cultural significance, captivated my imagination and sparked a deep curiosity about our ancestors artistic expressions and symbolic meanings.The basin, dating back to the Neolithic Age, is a testament to the artistic prowess of our ancestors. Its surface is adorned with a unique pattern that features a fish with a human face, an image that seems to bridge the gap between the natural and the supernatural. The craftsmanship is exquisite, with the fishs scales meticulously carved and the humanlike eyes conveying a sense of depth and emotion that is rare in such ancient art.As I stood before the basin, I couldnt help but wonder about the story behind this piece. Our guide, a knowledgeable historian, explained that the humanfaced fish is believed to symbolize the harmony between humans and nature. The fish, being a creature of water, represents the lifegiving element, while the human face signifies the intelligence and emotions of mankind. The fusion of these two elements in a single image suggests a deep respect for the interconnectedness of all life.Moreover, the historian shared that such artifacts were not merely decorative but held ritualistic significance. The basin might have been used in ceremonies to honor the gods of water and fertility, reflecting the importance of water in sustaining life and ensuring a bountiful harvest. Thehumanfaced fish could have been a central figure in these rituals, embodying the hopes and prayers of the community.The visit to the museum was not just an educational experience it was a journey into the past that allowed me to appreciate the rich cultural heritage of our ancestors. The humanfaced fish pattern basin, in particular, left a lasting impression on me. It was a reminder that art has always been a means of communication, a way to express complex ideas and emotions that transcend time and space.In todays world, where technology and modernity often overshadow our connection to nature, the basin serves as a poignant reminder of our roots. It urges us to reflect on our relationship with the environment and to consider the impact of our actions on the world around us. The ancient artists who created this piece were not just skilled craftsmen they were visionaries who understood the importance of balance and harmony in life.As I left the museum that day, I felt a renewed sense of awe for the human spirit and its ability to create beauty and meaning in even the simplest of forms. The humanfaced fish pattern basin is more than just an artifact it is a window into the soul of our ancestors, a glimpse into a world where art and life were deeply intertwined.In conclusion, the humanfaced fish pattern basin is a remarkable piece of art that speaks volumes about the cultural and spiritual beliefs of our ancient forebears. It is a symbol of unity between humans and nature, a representation of the profound respect for life, and a testament to theenduring power of artistic expression. As a high school student, I am grateful for the opportunity to have encountered such a significant piece of history, and I am inspired to continue exploring the rich tapestry of human culture and creativity.。

The characteristics of enriched nitrifier culture

The characteristics of enriched nitrifier culture

Journal of Hazardous Materials 171 (2009) 1051–1057Contents lists available at ScienceDirectJournal of HazardousMaterialsj o u r n a l h o m e p a g e :w w w.e l s e v i e r.c o m /l o c a t e /j h a z m atThe characteristics of enriched nitrifier culture in the degradation of selected pharmaceutically active compoundsNgoc Han Tran a ,∗,Taro Urase b ,Osamu Kusakabe aa Department of Civil Engineering,Tokyo Institute of Technology,Ookayama 2-12-1,Meguro,Tokyo 152-8552,Japan bSchool of Bioscience and Biotech,Tokyo University of Technology,Katakura 1401-1,Hachioji,Tokyo 192-0982,Japana r t i c l e i n f o Article history:Received 21January 2009Received in revised form 22May 2009Accepted 19June 2009Available online 27 June 2009Keywords:Activated sludge DegradationEnriched nitrifier culture Pharmaceuticalsa b s t r a c tThe biodegradation of 10selected pharmaceuticals by enriched nitrifier cultures with ammonia oxidizing activity of 30mg NH 4-N/g MLVSS h was investigated under various initial operating conditions such as in the presence of different growth substrates and inhibitors.The enriched nitrifier culture showed higher degradation of the target pharmaceuticals than the conventional activated sludge.The degradation effi-ciency of persistent pharmaceuticals such as clofibric acid (CA),diclofenac (DCF),carbamazepine (CBZ),and propyphenazone (PPZ)was increased with the increase in the ammonium concentration.A higher removal efficiency of CA,DCF,CBZ and PPZ was obtained when organic substrates were added.The contri-bution of autotrophs and heterotrophs in the biotransformation of the pharmaceuticals by the enriched nitrifier culture was successfully estimated by the addition of inhibitors.Experimental results showed that the high degradation of IBP and partial degradation of other selected pharmaceuticals were observed in the presence of allylthiourea (ATU),an ammonia monooxygenase inhibitor,reflecting the activity of heterotrophic bacteria,while the results with and without ATU addition showed that the contribution of the nitrification in the degradation of most pharmaceuticals was also dominant.The results suggest that nitrification can enhance the biotransformation of pharmaceutical substances.© 2009 Elsevier B.V. All rights reserved.1.IntroductionThe occurrence and fate of pharmaceutically active compounds (PhACs)in the water environment have been recognized as one of the emerging issues in environmental chemistry due to their poten-tial to cause undesirable ecological and human health effects [1,2].PhACs have been detected ubiquitously in water environments and water distribution systems because of their high persistence and low adsorption properties.For example,carbamazepine has been detected in groundwater [3]and diclofenac was also found in tap water in Berlin [4].The removal of PhACs in water and wastewa-ter treatment is essential to prevent environmental contamination and possible adverse effects.Because these chemicals are often present in wastewater at concentrations in the low ␮g/l range or less [5,6]they cannot support cell growth and activity of organisms capable of mineralizing these compounds in biological wastewater treatment.The biodegradation of PhACs in wastewater is likely to be due to cometabolic activity.This means that PhACs can only be degraded∗Corresponding author.Tel.:+81357342798;fax:+81357343577.E-mail address:hantn04779@ (N.H.Tran).in the obligate presence of a primary substrate (growth support-ing substrate).Published reports on the cometabolism of PhACs are currently limited.Several studies on the removal of xenobi-otics have shown that the degradation can be enhanced by the augmentation through the addition of organic carbon sources or other nutrient substances such as nitrogen,and phosphate as well as mineral constituents [7,8].It was also suggested that primary substrates not only serve to sustain biomass production but also act as an electron donor for the cometabolism of the non-growth substrate [9].Several recent studies reported that the ammonia oxi-dizing bacteria (AOB)in nitrifying activated sludge system were responsible for the elimination of these chemicals in wastew-ater [10,11].The cometabolism of PhACs may be important in the degradation of PhACs because AMO (ammonium monooxy-genase)has a relatively wide spectrum for the degradation of substrates.Therefore,in this study in order to clarify the role of nitrifica-tion in the degradation of PhACs,an enriched nitrifier culture was prepared from activated sludge.The objectives of this study were to investigate the effect of supplement of the primary substrates (ammonium and organic substrates)on the biodegradability of the selected PhACs by enriched nitrifier culture and estimate the role of nitrification in the degradation of PhACs in biological wastewater treatment.0304-3894/$–see front matter © 2009 Elsevier B.V. All rights reserved.doi:10.1016/j.jhazmat.2009.06.1141052N.H.Tran et al./Journal of Hazardous Materials 171 (2009) 1051–10572.Materials and methods 2.1.Chemicals and mediaThe chemicals used in this study were purchased from Kanto-Kagaku,Japan.The composition of mineral-salts medium (MSM)was:Na 2CO 31514mg/l;MgSO 4·7H 2O 41.6mg/l;CaCl 2·2H 2O 50mg/l;NaH 2PO 450.5mg/l;K 2HPO 4·3H 2O 75.6mg/l;CuSO 4·5H 2O 0.5mg/l;FeCl 3·6H 2O 0.5mg/l and ZnSO 4·H 2O 0.5mg/l.The MSM was used with other supplements such as ammonium,organic substrates and target PhACs according to the experimental purposes.The target compounds used in this study were 10selected pharmaceutical compounds clofibric acid (CA),gemfibrozil (GFZ),ibuprofen (IBP),fenoprofen (FEP),ketoprofen (KEP),naproxen (NPX),diclofenac (DCF),indomethacin (IDM),propyphenazone (PPZ)and carbamazepine (CBZ).Table 1shows the chemicalstructures and physicochemical properties of these compounds [12].Mixed stock solution of 1g/l of the target pharmaceuticals was prepared in methanol and introduced in the MSM as necessary.2.2.Enrichment of nitrifying bacteriaActivated sludge with a low nitrifying activity of less than 5mg NH 4-N/g MLSS h was collected from a nitrification tank at a munic-ipal wastewater treatment plant in Japan.From this collection,nitrifiers were enriched in fill-and-draw operation with a 2d-cycle in a 2-l reactor at 30◦C for more than 2months.At the start of enrichment,activated sludge and the MSM solution supplemented with ammonium were used as enrichment medium.The ammo-nium concentration was gradually increased from 100to 300mg NH 4-N/l during the enrichment period depending on the growth in the nitrifying activity of the sludge.The pH in the reactor was con-Table 1The physicochemical properties and chemical structure of the target compounds by Ternes and Joss [12].Target compoundsChemical structureMol.weightlog K owp K aHenry’s coefficientCA 241.65 2.57 3.02.19×10−8GFZ 250.34 4.8n.a.n.a.IBP 206.29 3.97 4.911.50×10−7FEP 242.28 3.9 4.5n.a.KEP 254.29 3.12 4.52.12×10−11NPX 230.27 3.2 4.23.39×10−10DCF 296.16 4.5 4.154.73×10−12IDM 357.80 4.27 4.503.13×10−14PPZ 230.31 1.94–1.84×10−9CBZ 236.28 2.45–1.08×10−10n.a.:data not available.(–):not applicable.N.H.Tran et al./Journal of Hazardous Materials171 (2009) 1051–10571053trolled at7.5–8.0using NaHCO330g/pressed air was used to aerate the culture to maintain a dissolved oxygen level of6.0mg O2/l or higher.Conventional activated sludge(CAS)taken from another municipal wastewater treatment plant in Japan was also used in the experiment for a comparison with nitrifying activated sludge (NAS).2.3.Batch degradation experiments of PhACsSterilized300ml Erlenmeyerflasks were eachfilled with100ml of MSM supplemented with various initial ammonium or sodium acetate concentrations depending on the experimental purposes. The target pharmaceuticals in methanol solution were then added to theflasks to achieve an initial concentration of100␮g/l.The amount of the biomass in theflasks was adjusted to achieve an MLSS concentration of1000mg/l at the beginning of all batch tests.The pH of the culture medium was kept at approximately7.5–8.0using NaHCO330g/l during cultivation period.The suspension in the flasks was cultivated in a temperature-controlled incubator at30◦C. Shaking ensured a sufficient supply of oxygen to keep the dissolved oxygen concentration higher than3mg/l.To suppress the degrading activities of PhACs by ammonia oxidation,10mg/l of allylthiourea (ATU)was added as the AMO(ammonia monooxygenase)inhibitor [13]with the ammonium-supplemented MSM in the case of the inhibition experiments for nitrifiers.The experiments with the full inhibition of biological activities were also carried out to distinguish pure adsorption onto sludge from biodegradation.The inactivation of sludge was performed with the addition of sodium azide(NaN3) at0.2%weight to volume(w/v)into the ammonium-supplemented MSM.During the batch degradation experiments,the target com-pounds and NH4-N,NO2-N,NO3-N,and COD concentrations were measured.All batch experiments were implemented in triplicate.2.4.AnalysesThe concentrations of the target pharmaceutical substances such as CA,GFZ,IBP,FEP,KEP,NPX,DCF,and IDM were measured by the method using gas chromatography–mass spectrome-try(GC/MS)after solid phase extraction and pentafluorobenzyl derivatization suggested by Koutsouba et al.[14]with slight modi-fications.Solid phase extraction disks(C18,47mm disk typefilter, 3M)were used to concentrate100ml of water sample to which two surrogates,2,3-dichlorophenoxyacetic acid and chrysene-d12, and hydrochloric acid for the pH adjustment at2were added. After the extraction,2,4-dichlorobenzoic acid was added to check the recovery in the pentafluorobenzyl derivatization step.GC/MS (Shimadzu,QP–5000)with DB-5MS column was used for the quan-tification of the derivatized material in toluene solution.PPZ and CBZ,which require no derivatization in the analysis,were quanti-fied in the same chromatogram.Concentrations of NH4-N,NO2-N, NO3-N,and COD after heating with K2Cr2O7solution were deter-mined using the colorimetric tests following the protocol of HACH DR-2010.3.Results and discussion3.1.Enrichment of nitrifying bacteriaTo obtain a nitrifier-dominated population in the sludge,the enrichment was performed for more than2months.Ammonium oxidizing activity estimated from the disappearance rate of ammo-nium gradually increased and achieved30mg NH4-N/g MLVSS h after2months of enrichment.During the experimental period, the nitrifying activity of this sludge was maintained at around 25–30mg NH4-N/g MLVSS h.The volatile fraction of the nitrifying activated sludge was70±10%of total suspended solids.This nitrify-ing activated sludge(NAS)was used for the following experimental purposes.3.2.Degradation kinetics of selected pharmaceuticals in batch experimentsFig.1shows representative results obtained for the removal of selected pharmaceuticals in batch experiments.The batch experi-ment shown in Fig.1was performed with enriched nitrifier culture at an initial concentration of100␮g/l for all selected pharmaceu-ticals and NH4-N100mg/l.Exponential decreases in concentration over time were observed for all target compounds.In previous batch degradation studies using activated sludge spiked with selected pharmaceuticals it has been reported that the degradation of pharmaceuticals in the water phase can be described by a pseudo-first-order degradation kinetics[15–18]as given in Eq.(1):dC wdt=−k biol·X·C w(1) where C w is the concentration of the target substances in the water phase(␮g/l),t is the time(day),k biol is thefirst-order biodegrada-tion constant(l/g MLSS day),and X is the mixed liquor suspended solids concentration(g MLSS/l).Rearranging Eq.(1),the following equation is obtained,lnC wC o=−k biol X·t(2)where C o is the initial concentration of the selected pharmaceuti-cals in the water phase(␮g/l).This equation suggests that a plot of ln(C w/C o)versus X·t yields a straight line andfirst-order biodegra-dation constant k biol is obtained from the slope of the straight line by applying the least-squares method.Thefirst-order biodegrada-tion constants of selected pharmaceuticals in the water phase were calculated and are shown in Table2.The comparison of biodegradation constants shows that IBP was removed rapidly.This result is consistent with previous publica-tions[15–17,19].The estimated k biol for IDM,CBZ and DCF was slightly higher than those reported in the literature[16–18],while the calculated k biol for CA,GFZ,FEP,and IBP was significantly smaller than those reported by Joss et al.[16].This difference is probably due to aspects of the sludge composition such as biodiversity of biomass, types of primary substrates,fraction of active biomass withinthe Fig.1.Changes in normalized concentrations of selected pharmaceuticals during batch experiment using enriched nitrifier culture(NAS).1054N.H.Tran et al./Journal of Hazardous Materials 171 (2009) 1051–1057Table 2First-order biodegradation constants k biol of selected pharmaceuticals observed in batch experiments with enriched nitrifier culture (NAS).Target compoundBiodegradation constants (k biol )NAS (l/g MLSS day)aCAS (l/g MLSS day)b MBR (l/g SS day)c CAS (l/g SS day)d MBR (l/g SS day)e CA 0.03–0.070.0120.1–0.230.3–0.80.09±0.033GFZ 1.01–1.840.0620.5–1.8 6.4–9.6n.a.IBP 3.24–4.010.2099–2221–35>3FEP 1.18–1.670.110 3.3–5.910–14n.a.KEP 0.68–1.590.031n.a.n.a.n.a.NPX 0.39–0.930.0050.4–0.8 1.0–1.90.08±0.016DCF 0.31–0.520.010≤0.1≤0.1<0.02IDM 1.14–1.620.444≤0.21≤0.3n.a.PPZ 0.08–0.170.024n.a.n.a.n.a.CBZ0.07–0.140.048n.a.n.a.<0.005The range indicates the 95%confidence interval obtained from thebatch experiments in this study and previous research [16].The sign “±”indicates standard errors.The sign “≤”indicates that the lower limit was beyond experimental resolution [16];n.a.:data not available.aNAS:k biol for enriched nitrifier culture in this study.bCAS:k biol for conventional activated sludge [17].cMBR c :k biol for sludge taken pilot-scale membrane bioreactor [16].dCAS:k biol for sludge taken from full-scale conventional activated sludge process [16].eMBR:k biol for sludge taken from single-house membrane bioreactor at Experiment 2[18].Fig.2.Changes in NH 4-N and NO 3-N concentrations during the degradation of PhACs by CAS and NAS cultures.total mixed liquor suspended solids,and the floc size of the sludge [16,20,21].In addition the difference in the initial concentration of selected pharmaceuticals and the experimental conditions may have an influence.3.3.Degradation of PhACs by conventional activated sludgeThe elimination of pharmaceuticals by conventional activated sludge (CAS)has been repeatedly studied and those studies have shown that the removal efficiency of pharmaceuticals was gener-ally low,especially for persistent pharmaceuticals such as CA,DCF,CBZ and PPZ of which removal efficiency was around 5–20%[22].To illustrate whether there is any advantage to the NAS system compared with the CAS system in the PhACs degradation,a lab-oratory study was implemented with NAS and CAS systems under the same initial operating conditions with MLSS concentration of 1000mg/l,NH 4-N 100mg/l and without acetate as an organic sub-strate.In this study,an NAS system with nitrifying activity of 30mg NH 4-N/g MLVSS obtained from the enrichment process was used to ensure stable nitrification.The representative results on nitrifi-cation are shown in Fig.2.Although initial nitrifying activity was higher in the case of NAS than CAS,the nitrification was completed even within 6days in the cases of both NAS and CAS (Fig.2).The results on the PhACs degradation by NAS and CAS after 6days of operation are shown in Fig.3.The overall removal efficiencies for 10PhACs by the NAS system varied from 18%to 99.8%,in which 3of 10pharmaceuticals such as CA,CBZ and PPZ were removed at less than 40%efficiency (as shown in Fig.3),probably due to their lower hydrophobicity (log K ow <3)and chemical structure (Table 1).According to Kimura et al.[23]complicated chemical structures such as KEP an NPX were not removed during conventional treat-ment plants but were eliminated by membrane bioreactor [23].It was assumed that the poor removal was due to the presence of a complicated structure with two aromatic rings causing more resis-tance to the degradation process.Additionally,the presence of nitro and halogen groups in aromatic compounds probably results in a decreasing degradation rate [23,24].Our results also show that the removal efficiencies of IBP were 94%and 100%by CAS and NAS,respectively.This indicates that IBP at least as a parent compound was biodegradable with a very small difference between NAS and CAS.In contrastto the case of IBP,the removal efficiency of other pharmaceuticals such as CA,DCF,CBZ,and PPZ by CAS was very low,while NAS displayed considerable removal efficiencies.The persistence of these compounds in sewage treatment plants was repeatedly reported by several studies [16,22].The advantages of the use of nitrifiers in the degradation of persistent organic pollu-tants were reported in several recent studies [10,11,15].A detailed monitoring in a full scale plant shows that the total concentra-tion of 66pharmaceuticals in the effluent from the CAS process was 1.5times higher than that from a biological nutrient removalparison of the removal efficiency of PhACs by CAS and NAS cultures.Error bars represent the standard deviation of three triplicates.N.H.Tran et al./Journal of Hazardous Materials171 (2009) 1051–10571055Fig.4.Effect of initial ammonium concentration on the degradation of PhACs.Error bars represent the standard deviation of three replicates.process[25].The high removal under nitrification may be caused by the diversity of nitrifiers and a variety of non-specific mono-and dioxygenase enzymes associated with both heterotrophic and autotrophic microorganisms.Recent studies also found that AMO played an important role in the conversion of remarkably broad substrates including trichloroethylene,alkanes,alkenes,aromatic derivatives,several heterocyclic compounds,and some heteroatom ring compounds[10,11,13,26].Taken together,the results may suggest that the removal effi-ciency of pharmaceuticals in biological wastewater treatment not only depends on the chemical characteristics of target pharma-ceuticals but also relies on the microbial species especially on the nitrifiers involved.3.4.Effect of initial ammonium concentrations on thedegradation of PhACsTo determine the effect of ammonium concentration(as a pri-mary substrate)on the cometabolic activity of PhACs by NAS,a series of batch biodegradation experiments under the different ini-tial ammonium concentrations ranging from20to200NH4-N/l were conducted.Fig.4shows the biodegradation of100␮g/l PhACs by NAS with various initial ammonium concentrations after6days of cultivation.From Fig.4,it can be concluded that the removal efficiency of the PhACs increased with the increase in the initial ammonia concentration.In particular,the removal of persistent PhACs such as CA,DCF,CBZ,and PPZ was enhanced at higher initial ammonia concentrations.At lower initial ammonium concentra-tions,smaller cometabolic activity was probably responsible for the slower degradation of some pharmaceuticals.Although the amounts of NH4-N consumed doubled in the cases between NH4-N100mg/l and200mg/l,the removal of PhACs did not increase so much.The rate of the degradation would be dependent on the amount of AMO induced.3.5.Effect of addition of organic substrates on the degradation of PhACsGenerally speaking,autotrophs are responsible for nitrification, although heterotrophs are also known to function as nitrifiers[27]. In addition,heterotrophs can use organic compounds synthesized by autotrophs in the NAS system in this study.To clarify the role of heterotrophs,the addition of sodium acetate(a primary substrate supporting for the growth of heterotrophic bacteria contained in an NAS system)with different initial acetate concentrations ranging from0to100mg CH3COO−/l was examined without the supply of ammonium.The results are summarized in Table3and Fig.5.Fig.5shows the biodegradation efficiencies of100␮g/l PhACs by NAS after6days for the different acetate concentration addi-tions.Without acetate addition,in the case that only NAS and the selected PhACs diluted in methanol were added into MSM medium, the biodegradation of the selected PhACs such as CA,DCF,CBZ,and PPZ was not significant while IBP and FEP displayed considerable biodegradation efficiencies.In this case,methanol is considered as a carbon source supporting the growth of the heterotrophic microorganisms contained in the NAS.On the other hand,a sig-nificantly higher biodegradation efficiency of PhACs was observed in the case of acetate addition.Table3also shows the increase in the biomass concentration during the batch experiment caused by both acetate and methanol,carbon and energy sources supporting the Table3Changes in COD,and MLSS concentrations during the batch experiments of organic substrate addition.Acetate dosage(mg CH3COO−/l)Initial COD(mg/l)Final COD(mg/l) MLSS(mg/l)0108±610±2132±22 50162±88±2237±21 100209±512±3350±241056N.H.Tran et al./Journal of Hazardous Materials171 (2009) 1051–1057Fig.5.Effect of initial acetate concentration on the degradation of PhACs.Error bars represent the standard deviation of threereplicates.Fig.6.Changes in NH 4-N,NO 3-N and COD concentrations during the degradation of PhACs by NAS with and without inhibitors.growth of heterotrophic microorganisms in the enriched nitrifier culture.Urase and Kikuta [17]reported that the removal of pharmaceu-ticals was greater in the case of low organic substrate concentration in the batch experiment using conventional activated sludge.The opposite result of this study may be due to the difference in the sludge population and the amount of enzymes induced at the start of the batch experiment.In the NAS system,the amount of enzymes responsible for the degradation by heterotrophs was not enough at the start of batch experiments,because the MSM used in the enrichment period did not include any organic substrate.Conse-quently in the NAS system,the degradation of PhACs was promoted by the organic substrates by the induction of the enzymes.On the other hand,in the CAS system,PhACs could compete with organic substrates in the degradation because the enzymes had already been induced at the start of the batch experiments.Although the amount of enzymes induced before the start of the batch exper-iment affected the results,there are several researches showing the increase in the removal efficiency of micropollutants with higher organic substrate concentrations.Alexy et al.[28]foundthat partial biodegradation of 18biologically persistent antibiotics was observed when sodium acetate was also present.Ziagova and Liakopoulou-Kyriakides [29]reported that the degradation of 2,4-dichlorophenol was enhanced by the addition of glucose.3.6.Degradation of PhACs by enriched nitrifier culture in the presence of inhibitorsTo reinforce the contributive role of the nitrification process in the degradation of PhACs by NAS,two inhibitory reagents were used to confirm whether the removal of pharmaceuticals arose from the biological activity of sludge,particularly from the activity of ammo-nia oxidizing bacteria (AOB)community.ATU and NaN 3were used to inhibit ammonium oxidation activity and the complete biological activity of sludge,respectively.As shown in Fig.6,without inhibitors,the ammonium in the solution was converted to nitrate,and the total nitrogen con-centrations were nearly constant.In contrast,in the case of ATU addition,the nitrification was negligible however,COD concen-tration decreased significantly from 102to 8mg/l duringtheFig.7.Removal of the PhACs by NAS with and without inhibitors.Error bars represent the standard deviation of three triplicates.N.H.Tran et al./Journal of Hazardous Materials171 (2009) 1051–10571057experimental period due to the degradation of methanol added as the solvent for the pharmaceuticals.The differences between the results of the experiments with and without ATU addition in Fig.7 can be interpreted as being due to biodegradation by nitrification. Because ATU is only an inhibitor of ammonia monooxygenase in ammonia oxidizing bacteria,the high degradation of IBP and par-tial degradation of other selected PhACs such as GFZ,KEP,FEP,NPX, IDM and DCF were observed during the degradation period prob-ably due to the activity of heterotrophs.The degradation of IBP in the enriched nitrifier culture was mainly dependent on the activity of heterotrophic microorganisms.That is why CAS in the previous study[16]can degrade IBP much faster than NAS in this study.In the case of NaN3addition,the changes in pharmaceuti-cals concentrations were not significant.Sodium azide inactivates almost all of the biological activity of microorganisms,and thus the removal of the pharmaceuticals in the experiment with NaN3was caused solely by adsorption onto sludgeflocs without biological degradation.Although sodium azide may alter the surface char-acteristics/adsorptive capacity of sludgeflocs,the low adsorption of the pharmaceuticals onto sludge in the batch experiment was consistent with the previous study[17].4.ConclusionThe biodegradation of10selected pharmaceuticals by enriched nitrifier cultures with ammonia oxidizing activity of30mg NH4-N/g MLVSS h was investigated under various operating conditions. Obvious advantages of the enriched culture of nitrifier over the conventional activated sludge were recognized with most of the selected pharmaceutical substances tested.In particular,the per-sistent pharmaceuticals such as DCF,NPX,CBZ and PPZ were removed by enriched nitrifier culture more efficiently than by the conventional activated sludge.The experimental results have demonstrated that the high removal efficiency of pharmaceuti-cals was observed under the supplement of growth substrates (ammonium and organic substrates)probably depending on the amount of enzymes induced.The addition of ATU,an ammonia monooxygenase inhibitor,inhibited the nitrification completely and suppressed the removal of most selected pharmaceuticals.The partial biotransformation of ibuprofen and other selected PhACs in the presence of ATU may be due to the activity of heterotrophic microorganisms in the enriched nitrifier culture.In conclusion,the results taken together suggest that the elimination of selected pharmaceuticals can be enhanced by nitri-fication.The enrichment of nitrifier-dominated culture to achieve stable nitrification in the activated sludge may have an advantage in enhancing the removal efficiency of organic micropollutants. References[1]C.G.Daughton,T.A.Ternes,Pharmaceuticals and personal care products in theenvironment:agents of subtle change?Environ.Health Perspect.107(1999) 907–937.[2]K.Kümmerer,Drugs in the environment:emission of drugs,diagnostic aidsand disinfectants into wastewater by hospitals in relation to other sources—a review,Chemosphere45(2001)957–969.[3]J.E.Drewes,T.Heberer,K.Reddersen,Fate of pharmaceuticals during indirectpotable reuse,Water Sci.Technol.46(2002)73–80.[4]T.Heberer,K.Reddersen,A.Mechlinski,From municipal sewage to drinkingwater:fate and removal of pharmaceutical residues in the aquatic environment in urban areas,Water Sci.Technol.3(2002)81–88.[5]D.W.Kolpin,E.T.Furlong,M.T.Meyer,E.M.Thurman,S.D.Zaugg,L.B.Barber,H.T.Buxton,Pharmaceuticals,hormones,and other organic wastewater con-taminants in U.S.Streams,1999–2000:a national reconnaissance,Environ.Sci.Technol.36(2002)1202–1211.[6]S.T.Glassmeyer,E.T.Furlong,D.W.Kolpin,J.D.Cahill,S.D.Zaugg,S.L.Werner,M.T.Meyer,D.D.Kryak,Transport of chemical and microbial compounds from known wastewater discharges:potential for use as indicators of human fecal contamination,Environ.Sci.Technol.39(2005)5157–5169.[7]A.Boiesen,E.Arvin,K.Broholm,Effect of mineral nutrients on the kinetics ofmethane utilization by methanotrophs,Biodegradation4(1993)163–170. [8]F.Fava,P.M.Armenante,D.Kafkewitz,L.Marchetti,Influence of organic andinorganic growth supplements on the aerobic biodegradation of chlorobenzoic acids,Appl.Microbiol.Biotechnol.43(1995)171–177.[9]P.S.Perkins,S.J.Komisar,J.A.Puhakka,J.F.Ferguson,Effects of electron donorsand inhibitors on reductive dechlorination of2,4,6-trichlorophenol,Water Res.28(1994)2101–2107.[10]A.L.Batt,S.Kim, D.S.Aga,Enhanced biodegradation of iopromide andtrimethoprim in nitrifying activated sludge,Environ.Sci.Technol.40(2006) 7367–7373.[11]T.Yi,W.F.Harper,The link between nitrification and biotransformation of17␣-ethinylestradiol,Environ.Sci.Technol.41(2007)4311–4316.[12]T.A.Ternes,A.Joss,Human Pharmaceuticals,Hormones and Fragrances:TheChallenge of Micropollutants in Urban Water Management,IWA Publishing, London,UK,2006.[13]M.E.Rasche,M.R.Hyman,D.J.Arp,Factors limiting aliphatic chlorocarbondegradation by Nitrosomonas europaea:cometabolic inactivation of ammonia monooxygenase and substrate specificity,Appl.Environ.Microbiol.57(1991) 2986–2994.[14]V.Koutsouba,T.Heberer,B.Fuhrmann,K.Schmidt-Baumler,D.Tsipi,A.Hiskia,Determination of polar pharmaceuticals in sewage water of Greece by gas chromatography–mass spectrometry,Chemosphere51(2003)69–75.[15]K.Kimura,H.Hara,Y.Watanabe,Elimination of selected acidic pharmaceuti-cals from municipal wastewater by an activated sludge system and membrane bioreactors,Environ.Sci.Technol.41(2007)3708–3714.[16]A.Joss,S.Zabczynski,A.Göbel,B.Hoffmann,D.Löffler,C.S.McArdell,T.A.Ternes,A.Thomsen,H.Siegrist,Biological degradation of pharmaceuticals in municipalwastewater treatment:proposing a classification scheme,Water Res.40(2006) 1686–1696.[17]T.Urase,T.Kikuta,Separate estimation of adsorption and degradation of phar-maceutical substances and estrogens in the activated sludge process,Water Res.39(2005)1289–1300.[18]C.Abegglen,A.Joss,C.S.McArdell,G.Fink,M.P.Schlüsener,T.A.Ternes,H.Siegrist,The fate of selected micropollutants in a single-house MBR,Water Res.43(2009)2036–2046.[19]J.B.Quintana,S.Weiss,T.Reemtsma,Pathways and metabolites of micro-bial degradation of selected acidic pharmaceutical and their occurrence in municipal wastewater treated by a membrane bioreactor,Water Res.39(2005) 2654–2664.[20]A.Joss,H.Andersen,T.Ternes,P.R.Richle,H.Siegrist,Removal of estrogensin municipal wastewater treatment under aerobic and anaerobic condi-tions:consequences for plant optimization,Environ.Sci.Technol.38(2004) 3047–3055.[21]M.Clara,N.Kreuzinger,B.Strenn,O.Gans,H.Kroiss,The solids retention time—asuitable design parameter to evaluate the capacity of wastewater treatment plants to remove micropollutants,Water Res.39(2005)97–106.[22]S.Suárez,M.Ramil,F.Omil,J.M.Lema,Removal of pharmaceutically activecompounds in nitrifying–denitrifying plants,Water Sci.Technol.52(2005) 9–14.[23]K.Kimura,H.Hara,Y.Watanabe,Removal of pharmaceutical compounds bysubmerged membrane bioreactors(MBRs),Desalination178(2005)135–140.[24]R.Andreozzi,R.Cesaro,R.Marotta,F.Pirozzi,Evaluation of biodegradationkinetic constants for aromatic compounds by means of aerobic batch exper-iments,Chemosphere62(2006)1431–1436.[25]T.Okuda,Y.Kobayashi,R.Nagao,N.Yamashita,H.Tanaka,S.Tanaka,S.Fujii,C.Konishi,I.Houwa,Removal efficiency of66pharmaceuticals during wastewater treatment process in Japan,Water Sci.Technol.57(2008)65–71.[26]S.W.Chang,M.R.Hyman,K.J.Williamson,Cooxidation of naphthalene and otherpolycyclic aromatic hydrocarbons by the nitrifying bacterium,Nitrosomonas europaea,Biodegradation13(2002)373–381.[27]T.Khin,A.P.Annachhatre,Novel microbial nitrogen removal processes,Biotech-nol.Adv.22(2004)519–532.[28]R.Alexy,T.Kümpel,K.Kümmerer,Assessment of degradation of18antibioticsin the closed bottle test,Chemosphere57(2004)505–512.[29]M.Ziagova,M.Liakopoulou-Kyriakides,Kinetics of2,4-dichlorophenol and4-Cl-m-cresol degradation by Pseudomonas sp.cultures in the presence of glucose, Chemosphere68(2007)921–927.。

新概念四-新概念英语第四册第44课-Patterns of culture

新概念四-新概念英语第四册第44课-Patterns of culture

新概念英语第四册第44课:Patterns of cultureLesson 44 Patterns of culture文化的模式First listen and then answer the following question.听录音,然后回答以下问题。

What influences us from the moment of birth?Custom has not commonly been regarded as a subject of great moment. The inner workings of our won brains we feel to be uniquely worthy of investigation, but custom, we have a way of thinking, is behaviour at its most commonplace. As a matter of fact, it is the other way around. Traditional custom, taken the world over, is a mass of detailed behaviour more astonishing than what any one person can ever evolve in individual actions, no matter how aberrant. Yet that is a rather trivial aspect of the matter. The fact of first-rate importance is the predominant role that custom plays in experience and in belief, and the very great varieties it may manifest.风俗一般未被认为是什么重要的课题。

萨丕尔-沃尔夫假说

萨丕尔-沃尔夫假说

萨丕尔-沃尔夫假设主要内容美国人萨丕尔及其弟子沃尔夫提出的有关语言与思维关系的假设是这个领域里至今为止最具争议的理论。

沃尔夫首先提出,所有高层次的思维都倚赖于语言。

说得更明白一些,就是语言决定思维,这就是语言决定论这一强假设。

由于语言在很多方面都有不同,沃尔夫还认为,使用不同语言的人对世界的感受和体验也不同,也就是说与他们的语言背景有关,这就是语言相对论。

Linguistic relativity stems from a question about the relationship between language and thought, about whether one's language determines the way one thinks. This question has given birth to a wide array of research within a variety of different disciplines, especially anthropology, cognitive science, linguistics, and philosophy. Among the most popular and controversial theories in this area of scholarly work is the theory of linguistic relativity(also known as the Sapir–Whorf hypothesis). An often cited "strong version" of the claim, first given by Lenneberg in 1953 proposes that the structure of our language in some way determines the way we perceive the world. A weaker version of this claim posits that language structure influences the world view adopted by the speakers of a given language, but does not determine it.[1]由萨丕尔-沃尔夫假设的这种强假设可以得出这样的结论:根本没有真正的翻译,学习者也不可能学会另一种文化区的语言,除非他抛弃了他自己的思维模式,并习得说目的语的本族语者的思维模式。

文化价值观差异对语言风格的影响

文化价值观差异对语言风格的影响

文化价值观差异对语言风格的影响-以中美两国对比为例摘要随着经济全球化的发展,中美两国之间的联系日益密切。

由于历史背景,地域,政治文化的不同,两国之间的价值观取向也有所差异。

文化价值观的不同,也产生了具有本国特色的语言风格。

本文主要从价值观的角度分析其对中美两国语言风格的影响。

中美两国的价值观核心以美国的个人主义与中国的集体主义为主,分析在这种价值观差异影响下产生的直接式与间接式语言风格。

本研究主要采用了参考文献法,举例法,引用法和归纳总结法。

由于前人对该课题的研究尚未全面,因此本研究仍然有一定的现实意义:在国际交往日益频繁的当代社会,深入了解中西方国家的文化差异是非常必要的。

在此背景下,本研究有助于全面并深入地了解中美文化差异,期望可以帮助人们更好地加深中美两国的交流与合作。

关键词:价值观,个人主义,集体主义,直接式语言风格,间接式语言风格The Influence of the Differences in Cultural Values on Language Styles--A Contrast between the Chinese and the AmericanAbstractWith the development of economic globalization, the contact between China and the United States is increasingly close. Due to the historical background, geographical, political and cultural differences, the values of the two countries are also different. And different values also produced its own language style.This research mainly analyzes the impact of the different values for Chinese and American language style. The core values of the two country is individualism of the United States and collectivism of China. In this different values impact, analyzing American direct language style and Chinese indirect language style.In the process of writing this thesis, the concrete methods the author adopted include collecting materials from reference books, surfing on the internet to find helpful materials. Research method include using contrast, examples and analysis to support my thesis and inductive and summary method.Because of the previous research on this topic is not yet comprehensive, so this research still has certain practical significance.In contemporary society, the international communication is becoming more and more closely, it is necessary to understand the cultural differences between Chinese and Western countries.In this context, this study will help to understand the cultural differences between China and the United States comprehensively and deeply, and the author hopes it can help us to deepen the exchanges and cooperation between China and the United States.Key Words:different value; individualism; collectivism; direct language style indirect language styleChapter One Introduction1.1 Background of StudyDifferent countries have their own unique cultural value systems, and every cultural value system has its core values system. Different cultural values system has also formed a completely different language features. As the carrier of the culture, language is also has their own characteristics in the different cultural value. The language style of the United States, which is the mainstream of Western, is more directly and openly.Andas the representation of Eastern civilization, the language style of China is more indirect, subtle and tactful. An important reason of this is the different cultural value between the United States and China. That is the different core between Chinese and American cultural value1.2 Significance of This ResearchWith the development of economic globalization, the communication between China and the United States is becoming more and more closely. Understanding of the language style differences between the two countries will contribute to the exchanges and cooperation between the two countries. So that people can have a more comprehensive and profound understanding of Chinese and American cultural value and language style.However, the previous research is mostly about the differences between China and the United States cultural value or the differences between China and the United States language style, but for the influenceof the differences in cultural values on language stylesis not yet comprehensive.So this subject still has room to do further research. The author hopes this research can make English language learning becoming more regular, so that people can get more interests in English learning. And it can alsohelp people to deepen the exchanges and cooperation between China and the United States.The prior theories and opinions provide the author with basic ideas from these respects: the conceptualizing of the cultural value and language style, characteristics,origin and performance of American and Chinese cultural values, the characteristics and performance ofAmerican and Chinese language style.1.3 Research MethodsIn the process of writing this thesis, the concrete methods the author adopted include collecting materials from reference books, surfing on the internet to find helpful materials. Research method include using contrast, examples and analysis to support my thesis and inductive and summary method.Chapter Two Literature ReviewValue is the core of culture, and it dominates people's beliefs, attitudes, and opinions and become s the guide to people‟s action.Under the impact of different values, its culture also showed great differences.The obvious difference between American culture and Chinese culture is that the former emphasizes individual freedom, while the latter pays attention to the social relations.In this century, many scholars have studied and analyzed Chinese collectivism and individualism culture values in many aspects.Chinese language style is very prominently different with the United States language style, one of the most obvious difference is China's indirect language style and American style direct language. And many people have also been analyzed and discussed about the differences between this.2.1 Conceptualizing Cultural Value and Language StyleThere have been many scholars have defined the cultural values and language style. Their views on these issues may not necessarily identical, but also have their own unique perspective.2.1.1.Conceptualizing Cultural ValueIn An Inter-culturalComparison between Sino-American Cultural Value, the writer Li Mingming thinks that “Value is the consideration and evaluation to what is center of culture. Values aretheorientingconsiderationandevaluationtowhat is acceptable and what is not. Values influ ence people‟s behavior and thinking patterns. It guides our behavior patterns in communication.”(Li Mingming, 2007). He believes that value and culture are closely related. Like the American anthropologists Nanda and Warms proposed that“Values are shared ideas about what is true, right and beautiful that underlies cultural patterns and guide society in response to the physical and social environment” (Nanda and Warms 49).The value is the core of the culture, the formation of human value system cannot be separated from the culture, and values also reflects the characteristics of culture.In Sino-American Cultural Value—Differences and Mutual Understanding written by Li Qiao, the author is more inclined to think that value originates from social life.He quotes William‟s words as a proof of his point of view—“They prescribe which actions and ways of being are better than others; they are not descriptions of fact, but possess content and emotion and contribute to social reality." (Williams, 1970). He thinks that value is the rules of people‟s behavior or the social life. “These …rules‟ and guideposts are normative and teach us what is useful, good, right,wrong, what to strive for, how to live our life, and even what to die for." (Samovar, Porter and Stefani, 2000). No matter what the values are, people‟s thinking and behavior that in this society should be guided and influenced.2.1.2.Conceptualizing Language StyleEvery nation in the world has its own language style,which is not separated from its historical culture, traditional ideas and life customs.Its formation is changing over time, but it spreads slowly until forever.In Comments on Chinese Mainland of the Definition and Essential Characteristics of “L anguage Style”, Zhang Demin and Gao Hang discussed that the definition of language style is not consistent, there are many different definition about language style. And they summed up theworks of linguistics, rhetoric and style in 20th Century to the definition of language style, there are eight versions of the follow: “Felicitous T heory”,“Unique Personality Theory”,“Integrated Features T heory”, “Style Atmosphere T heory”, “Means of Expression System Theory”, “General Variation T heory”, “Personalized Speech Theory”,and “Aesthetic Taste or Aesthetic Appearance T heory”(“措辞巧妙论”,“独创个性论”,“综合特点论”,“格调气氛论”,“表达手段体系论”,“常规变异论”,“言语个性论”和“审美趣味论或美学面貌论”)(张德明,高航2004). All of these versions are definitions of language style, but the emphasis on these definitions is different. At the end of the article, the author expresses his own opinion. “Language style is speech style,it is that people use language in a particular context, select the means of expression, to form a comprehensive performance features of the landscape style. In short, it is the speech characteristics of comprehensive performance of the style.”(语言风格即言语风格,是人们在特定的语境中运用语言,选择表达手段,形成综合特点所表现的风貌格调。

Kluckhohn-and-Strodtback’s-value-orientation

Kluckhohn-and-Strodtback’s-value-orientation

Kluckhohn and Strodtback’s value orientationThe Kluckhohns and Strodtbeck, after examining hundreds of cultures, reached the conclusion that people turn to their culture for answers to the following questions。

(1) What is the character of human nature? (2) What is the relation of humankind to nature?(3) What is the orientation toward time?(4)What is the value placed on activity?And (5)What is the relationship of people to each other?The answers to these crucial questions serve as the bases for the five value orientations that are at the heart of their approach. These five orientations might best be visualized as points on a continuum. As you move through these five orientations,you will undoubtedly notice some of the same characteristics discussed by Hofstede。

This is very understandable because both approaches are talking about meaningful values found in all cultures. Hence, both sets of researchers were bound to track many of the same patterns.Human Nature Orientation1. evil2。

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The antimicrobial resistance pattern of cultured human methanogensreflects the unique phylogenetic position of archaeaBe ´dis Dridi 1,Marie-Laure Fardeau 2,Bernard Ollivier 2,Didier Raoult 1and Michel Drancourt 1*1Unite ´de Recherche sur les Maladies Infectieuses et Tropicales Emergentes,UMR CNRS 6236IRD 3R198,IFR 48,Faculte ´de Me ´decine,Universite ´de la Me ´diterrane ´e,Marseille,France;2Laboratoire de Microbiologie et Biotechnologie des Environnements Chauds,UMR-D180,IRD,Universite ´de Provence et Universite ´de la Me ´diterrane ´e,Marseille,France*Corresponding author.Unite ´des Rickettsies,Faculte ´de Me ´decine,27Boulevard Jean Moulin,Cedex 5,France.Tel:+33-4-91-38-55-17;Fax:+33-4-91-38-77-72;E-mail:michel.drancourt@univmed.frReceived 17March 2011;returned 6May 2011;revised 20May 2011;accepted 24May 2011Objectives:Methanogenic archaea are constant members of the human oral and digestive microbiotaretrieved,in particular,from periodontitis lesions.The objective of the study was to determine their suscepti-bility to antimicrobials.Methods:Using the macrodilution method in Hungate tubes with optical microscope observation combinedwith monitoring methane production,we determined the antibiotic resistance characteristics of eight metha-nogenic archaea.Results:Methanobrevibacter smithii strains were resistant to ampicillin,streptomycin,gentamicin,rifampicin,ofloxacin,tetracycline and amphotericin B,with MICs ≥100mg/L;these strains were also highly resistant tovancomycin (MIC ≥50mg/L).They were moderately resistant to chloramphenicol (MIC ≤25mg/L),and weresusceptible to bacitracin (MIC ≤4mg/L),metronidazole,ornidazole and squalamine (MIC ≤1mg/L).The suscep-tibility of Methanosphaera stadtmanae was the same as M.smithii ,except for chloramphenicol (MIC ≤4mg/L),and Methanobrevibacter oralis yielded the same data as M.smithii ,except for bacitracin (MIC ≤25mg/L).Theantibiotic susceptibility pattern of ‘Methanomassiliicoccus luminyensis ’,which was recently isolated fromhuman faeces,was identical to that of M.smithii .Conclusions:Human methanogenic archaea are highly resistant to antibiotics,being susceptible only to mol-ecules that are also effective against both bacteria and eukarya.Methanogenic archaea are good candidates totest for antimicrobial activity against members of this unique domain of life.Further studies to develop newmolecules specifically targeting archaea as potential causes of infection are warranted.Keywords:Methanobrevibacter smithii ,Methanosphaera stadtmanae ,Methanomassiliicoccus luminyensis ,Methanobrevibacter oralis ,methanogenic archaea,microbiota,antimicrobial agents,susceptibility testing,metronidazole,chloramphenicol,bacitracin,squalamineIntroduction Bacteria and archaea have long been classified together as pro-karyotes,but analysis of the ribosome by Carl Woese in 1974revealed that they form two distinct domains.1These data have since been confirmed by differences in the core genomes of bacteria,archaea and eukarya.2Within archaea and bacteria,metabolic processes are different,and the cell walls of archaea are different from those of bacteria,thus explaining why some antibiotics effective against bacteria are not effective againstarchaea.3,4The difficulty of cultivating methanogenic archaea has so far prevented a systematic evaluation of the antimicrobial agents that are active against both archaea and bacteria oreukarya.Only scarce data have been reported for Methanobrevi-bacter smithii (Mb.smithii )and Methanosphaera stadtmanae (Ms.stadtmanae );no systematic testing has been reported for Metha-nobrevibacter oralis (Mb.oralis ),which has been isolated on media containing cefalotin,clindamycin,kanamycin and vanco-mycin,5and no data have been published for ‘Methanomassilii-coccus luminyensis ’(Mm.luminyensis ),a new archaeon that we recently isolated from a human stool sample (Table 1).6–11Lastly,the fact that the archaea are a permanent feature of the human oral and digestive microbiota makes knowledge of the susceptibility of cultivable archaea to different antimicrobials #The Author 2011.Published by Oxford University Press on behalf of the British Society for Antimicrobial Chemotherapy.All rights reserved.For Permissions,please e-mail:journals.permissions@J Antimicrob Chemother 2011;66:2038–2044doi:10.1093/jac/dkr251Advance Access publication 16June 20112038 by guest on January 10, 2016/Downloaded fromTable 1.Summary of previous works on archaea and antibiotics with clinical relevance;only includes reports specifying the MICsOrganism Phylum Antibiotic,MIC (mg/L)Reference Methanococcus vannielii Euryarchaeota bacitracin (10)33chloramphenicol (100)penicillin G (2000)vancomycin (500)gentamicin (.500)6kanamycin (.500)neomycin (31)streptomycin (.500)tobramycin (.500)erythromycin (.500)chloramphenicol (0.5)tetracycline (125)anisomycin (500)rifampicin (250)ampicillin (.500)aureomycin (125)Methanosarcina barkeri Euryarchaeota gentamicin (.500)6kanamycin (.500)neomycin (2)streptomycin (.500)tobramycin (.500)erythromycin (.500)chloramphenicol (8)tetracycline (31)anisomycin (125)rifampicin (500)ampicillin (.500)aureomycin (31)novobiocin (200)9ciprofloxacin (100)Methanobrevibacter arboriphilus Euryarchaeota gentamicin (250)6kanamycin (500)neomycin (125)streptomycin (.500)tobramycin (250)erythromycin (500)chloramphenicol (2)tetracycline (500)anisomycin (2)rifampicin (500)ampicillin (.500)aureomycin (250)Methanobacterium bryantii Euryarchaeota gentamicin (125)6kanamycin (250)neomycin (125)streptomycin (.500)tobramycin (125)erythromycin (.500)chloramphenicol (2)tetracycline (250)anisomycin (2)rifampicin (500)ampicillin (.500)aureomycin (250)ContinuedArchaea resistance pattern 2039JACby guest on January 10, 2016/Downloaded fromessential.12In this study,we assessed the effectiveness against cultured human methanogenic archaea of different molecules used against eukarya or bacteria.Interestingly,we found that only agents with activity against both eukarya and bacteria had activity against cultured human methanogenic archaea.MethodsStrains and cultureMb.smithii ATCC35061T DSMZ861,Mb.smithii DSMZ2374,Mb.smithii DSMZ2375,Mb.smithii DSMZ11975,Mb.oralis DSMZ7256T andTable1.ContinuedOrganism Phylum Antibiotic,MIC(mg/L)ReferenceMethanobacterium ivanovii Euryarchaeota novobiocin(50)9ciprofloxacin(.200)Methanobacteriumthermoautotrophicum Euryarchaeota novobiocin(.200)9ciprofloxacin(—)Methanobacterium voltae Euryarchaeota novobiocin(100)9ciprofloxacin(—)Methanobacteriumthermolithotrophicus Euryarchaeota novobiocin(25)9ciprofloxacin(—)Halobacterium halobium and Halobacteriumcutirubrum Euryarchaeota gentamicin(.500)6kanamycin(.500)neomycin(.500)streptomycin(.500)tobramycin(.500)erythromycin(125)chloramphenicol(31)tetracycline(62)anisomycin(2)rifampicin(4)ampicillin(500)aureomycin(62)Halobacterium halobium Euryarchaeota novobiocin(10)9ciprofloxacin(.200)Natronobacterium gregoryi Euryarchaeota novobiocin(10)9ciprofloxacin(15)Sulfolobus acidocaldarius Crenarchaeota novobiocin(10)9ciprofloxacin(15)Methanobrevibacter smithii Euryarchaeota penicillin G(.64)11vancomycin(.64)cefalotin(.64)streptomycin(.64)gentamicin(.64)ciprofloxacin(.64)clindamycin(.64)metronidazole(0.5–64)Methanosphaera stadtmanae Euryarchaeota cefalotin(.1.7)20metronidazole(.1)clindamycin(.6.7)bacitracin(.10)trimethoprim(.10)methotrexate(.10)sulfanilamide(.500)Dridi et al.2040 by guest on January 10, 2016 / Downloaded fromMs.stadtmanae ATCC 43021T DSMZ 3091were purchased from the German Collection of Microorganisms and Cell Cultures (DSMZ,Braunsch-weig,Germany),and were grown on media 119and 322,depending on the strain (http://www.dsmz.de),at 378C in Hungate tubes (Dutscher,Issy-les-Moulineaux,France)under an H 2/CO 2(80/20)atmosphere withagitation.‘Mm.luminyensis ’CSUR P135T was isolated in our laboratoryfrom human stool samples and was cultivated using Methanobrevibacter medium (medium 119;http://www.dsmz.de)modified by the addition ofmethanol under a hydrogen atmosphere.Antimicrobial susceptibility testing Ampicillin,streptomycin,gentamicin,rifampicin,bacitracin,chloramphe-nicol,ofloxacin,tetracycline,amphotericin B and vancomycin were allobtained from Sigma (Saint Quentin Fallavier,France).Metronidazole and ornidazole were purchased from B.Braun Medical SAS (Boulogne,France).Squalamine was a gift from Jean-Michel Brunel,PharmacyFaculty,Marseilles,France.A filtered aqueous solution of each compound was anaerobically added to Hungate tubes containing distilled water,which were sterilized by autoclaving at 1218C for 15min under an N 2/CO 2(80/20)atmosphere.Susceptibility was determined by transferring500m L of an exponentially growing culture into 4.5mL of fresh medium containing 1,2,4,10,25,50or 100mg/L antibiotic and incubat-ing at 378C with agitation;the growth of archaea was observed after 5days of incubation.Control cultures were also incubated without anti-biotics to provide a baseline for the behaviour of the strains.Growth was assessed by optical microscope observation and by parallel methane production measurement using a GC-8A gas chromatograph (Shimadzu,Champs-sur-Marne,France)equipped with a thermal conduc-tivity detector and a Chromosorb WAW 80/100mesh SP100column (Alltech,Carquefou,France).N 2at a pressure of 100kPa was used asthe carrier gas.The detector and the injector temperatures were 2008C,and the column temperature was 1508C.To verify the antimicrobial activity of the tested antibiotics,the follow-ing control experiment was done.The culture media 119and 322(http://www.dsmz.de),and ‘Mm.luminyensis ’medium were supplemented with 1,2,4,10,25,50or 100mg/L antimicrobial compound,and were incu-bated at 378C in H 2/CO 2(80/20)atmosphere for 5days.Before incubation and on each day after incubation started,their activity was tested in a disc plate bioassay using clinical isolates of Escherichia coli and Staphylo-coccus aureus with known susceptibility patterns.Growth controls with adapted media instead of antibiotic dilutions were introduced in all experiments and all tests were done in triplicate.The MIC was defined as the lowest antibiotic concentration that inhibited methane production.Detection of b -lactamase activity was done using the cefinase test (Becton Dickinson,Le Pont de Claix,France).Bioinformatic analyses The Mb.smithii chloramphenicol O -acetyltransferase (Gene ID:5215732)was checked against GenBank using BlastP.A phylogenetic tree wasderived from sequence alignment using the maximum-likelihood algor-ithm in Mega ().Results and discussionThe activity of the tested antibiotics when incubated at 378C under an H 2/CO 2(80/20)atmosphere was confirmed by observ-ing the growth inhibition of E.coli and S.aureus ,which were used as controls,after 5days of incubation.As for Mb.smithii ,Ms.stadtmanae ,Mb.oralis and ‘Mm.luminyensis ’,all control cul-tures incubated without antibiotics grew as expected,with methane production starting on the third day.The four Mb.smithii strains under study were resistant to the tested ampicillin,streptomycin,gentamicin,rifampicin,ofloxacin,tetracycline and amphotericin B (MICs ≥100mg/L),and to van-comycin (MIC ≥50mg/L).These strains were moderately resist-ant to chloramphenicol (MIC ≤25mg/L),and were susceptible to bacitracin (MIC ≤4mg/L),metronidazole,ornidazole and squalamine,a new potent antimicrobial molecule 13–15(MIC ≤1mg/L)(Table 2).The antibiotic susceptibility pattern of ‘Mm.luminyensis ’was identical to that of Mb.smithii .Ms.stadtmanae exhibited the same resistance profile as Mb.smithii ,except for susceptibility to chloramphenicol (MIC ≤4mg/L).Mb.oralis yielded the same data as Mb.smithii ,except that it was moder-ately susceptible to bacitracin (MIC ≤25mg/L).No b -lactamase activity was detected in these organisms.The data reported herein extend previous knowledge on the antimicrobial susceptibility patterns of human methanogenic archaea (Table 1).Despite the fact that archaea and bacteria are quite similar in size and shape,most archaea have no cell Table 2.MICs (mg/L)of 13antimicrobial agents for four cultured human archaeaMb.smithii ATCC 35061T Mb.smithii F1strain DSMZ 2374Mb.smithii DSMZ 2375Mb.smithii B181strain DSMZ 11975Mb.oralis DSMZ 7256Ms.stadtmanae ATCC 43021T ‘Mm.luminyensis ’CSUR P135TAmphotericin B ≥100≥100≥100≥100≥100≥100≥100Ampicillin ≥100≥100≥100≥100≥100≥100≥100Streptomycin ≥100≥100≥100≥100≥100≥100≥100Gentamicin ≥100≥100≥100≥100≥100≥100≥100Rifampicin ≥100≥100≥100≥100≥100≥100≥100Ofloxacin ≥100≥100≥100≥100≥100≥100≥100Tetracycline ≥100≥100≥100≥100≥100≥100≥100Vancomycin ≥50≥50≥50≥50≥50≥50≥50Metronidazole ≤1≤1≤1≤1≤1≤1≤1Ornidazole ≤1≤1≤1≤1≤1≤1≤1Bacitracin ≤4≤4≤4≤4≤25≤4≤4Chloramphenicol ≤25≤25≤25≤25≤25≤4≤25Squalamine ≤1≤1≤1≤1≤1≤1≤1Archaea resistance pattern 2041JACby guest on January 10, 2016/Downloaded fromwall and the cell wall structure of the Methanobacteriales is uniquely composed of pseudomureins;also,the archaeal cell membrane is composed of glycerol-ether lipids.On the other hand,bacteria cell walls are mainly composed of peptidoglycans and their cell cytoplasmic membrane is composed of glycerol-ester lipids.3,4Accordingly,the tested archaea were resistant to cell wall inhibitors,including peptidoglycan inhibitors,the resistance to which had been previously reported.3,6,11,13The tested methanogens were also resistant to amphotericin B,in agreement with the absence of polyenes in archaeal walls.16Conversely,the tested archaea were susceptible to bacitracin,a previously reported inhibitor of pseudomurein-containing metha-nogens;17,18bacitracin forms complexes with intermediates of the pseudomurein lipid cycles and prevents the dephosphoryla-tion of polyisoprenoid pyrophosphate,which translocates build-ing blocks of the cell wall across the inner membrane.19It was previously established that bacitracin inhibits the growth of Mb.smithii and Ms.stadtmanae at 10mg/L.20,21Because of its 90100100100100910.02Methanosarcina acetivorans C2A (AE010299)Methanosarcina barkeri fusaro (CP000099)Methanosarcina mazei Go1 (AE008384)Methanobrevibacter ruminantium M1 (CP001719)Methanobrevibacter smithii (CP00078)Clostridium tetani (AE015927)Clostridium sporogenes (ZP02994193)Clostridium botulinum (FR773526)Bacteroides dorei (ZP03300675)Bacteroides vulgatus (CP000139)Bacteroides ovatus (NZADMO01000140)Paludibacter propionicigenes WB4 (CP002345)Klebsiella pneumoniae rhinoscleromatis (ZP06017720)Figure 1.A phylogenetic tree (maximum-likelihood algorithm)based on the chloramphenicol O -acetyltransferase gene sequence of the five archaeal strains harbouring the gene (625bp)and the corresponding region in eight bacteria having the enzyme with the higher sequence similarity (.90%)with Mb.smithii chloramphenicol O -acetyltransferase.The accession numbers (GI numbers for a complete genome)are indicated in the brackets.Only bootstraps of ≥90%are indicated.The scale bar represents a 2%nucleotide substitution rate.EukaryaBacteriaArchaeaA B D G H E FC IJKFigure 2.Activity spectrum of 11antimicrobial families against bacteria,eukarya and archaea,illustrating that the latter organisms are susceptible only to molecules also active against both bacteria and eukarya.A,amphotericin;B,rifampicin;C,quinolones;D,aminoglycosides;E,tetracyclines;F,chloramphenicol;G,glycopeptides;H,b -lactams;I,squalamine;J,azoles;and K,bacitracin.This figure appears in colour in the online version of JAC and in black and white in the print version of JAC .Dridi et al .2042 by guest on January 10, 2016/Downloaded fromsystemic toxicity,bacitracin is usable only as a local antibiotic for potential decontamination of vancomycin-resistant Enterococ-cus faecium 22,23and for treating Clostridium difficile -induced diarrhoea.24In addition,the tested methanogenic archaea were all susceptible to squalamine,a molecule exhibiting a depolarizing effect on Gram-positive bacteria,resulting in rapid cell death.14This molecule also directly interacts with the nega-tively charged phosphate groups in the Gram-negative bacterialouter membrane,leading to its disruption.14We further observed that the tested methanogens wereresistant to aminoglycosides and tetracyclines,two antibiotic families targeting the ribosome and interfering with the synthesis of proteins (Table 2).As for aminoglycosides,the Mb.smithii genome (NC_009515)17and the Ms.stadtmanae genome (NC_007681)18encode mutations in the rps 12p and L6genes that confer resistance to gentamicin and streptomycin,respectively,in bacteria.Chloramphenicol is another antibiotic that interferes with protein synthesis in the ribosome,and we observed that Mb.smithii ,‘Mm.luminyensis ’and Mb.oralis were resistant to chloramphenicol,in contrast to Ms.stadtma-nae ,using the criteria applied to anaerobic bacteria.25In vitro susceptibility to chloramphenicol has been previously reported,with MICs in the same range as determined here,6and we noticed for the first time that the Mb.smithii and the ‘Mm.lumi-nyensis ’genome,but not the Ms.stadtmanae genome,encode a chloramphenicol O -acetyltransferase,an enzyme inactivating chloramphenicol.Our bioinformatics analyses indicated that,among archaea,this enzyme is only present in six methanogenic organisms (Figure 1)and is more closely related to the one found in Clostridium species with a sequence similarity of 96%–100%(Figure 1).Whether these data support a potential lateral gene transfer between bacteria and archaea warrants further study.These data agree with the previously reported corpus of dataindicating the unique structure of the archaeal ribosome,as out-lined by the initial 16S rDNA sequence-based differentiation of this domain from those of bacteria and eukarya.1The tested methanogenic archaea were also resistant toantibiotics interfering with DNA replication and transcription,including rifampicin,as previously reported for Mb.smithii andMs.stadtmanae 6(Tables 1and 2).Rifampicin is a known inhibi-tor of the bacterial RNA polymerase 21and the archaeal RNA polymerase is structurally more closely related to the eukaryotic one.26Mb.smithii ,Ms.stadtmanae ,Mb.oralis and ‘Mm.lumi-nyensis ’were also resistant to ofloxacin,a fluoroquinoloneinhibitor of bacterial DNA replication and transcription (Table 2).This result agrees with the previous observation of a ciprofloxacin MIC of ≥100mg/L for seven different environ-mental archaea and of 15mg/L for Natronobacterium gregoryi .As this type II DNA topoisomerase is present in archaeal genomes,such high MICs are indicative of a very weak inter-action between the archaeal DNA gyrase-like enzyme and fluor-oquinolones.9Moreover,we observed that the Mb.smithii and Ms.stadtmanae genomes encode multidrug efflux systems,which could also contribute to the broad spectrum resistance of these organisms to antibiotics,including fluoroquinolones.On the other hand,all tested methanogenic archaea were sus-ceptible to imidazoles,the reduced derivatives of which directly interact with and break nucleic acids.27Metronidazole was pre-viously shown to inhibit unidentified faecal methanogens.11In the latter study,the MICs,which were between 0.5and 64mg/L,were below the faecal concentration of metronidazole achieved under therapeutic conditions,and the isolates were therefore all susceptible to metronidazole.11It was indeed observed that metronidazole treatment of the digestive tract in bone marrow transplant recipients eliminated detectable methanogens in the stool.28ConclusionsIn conclusion,we observed that the four tested methanogenic archaea were resistant to molecules that inhibit only bacteria or only eukarya,such as amphotericin B,but were susceptible to mol-ecules that were effective against both bacteria and eukarya (Figure 2),including imidazoles and squalamine.Indeed,metroni-dazole and other azoles were found to be active against bacteria,in the case of anaerobes,29and against eukarya,as in the case of Giardia lamblia ,30Entamoeba histolytica and Trichomonas vagina-lis .31Squalamine is a new potent antimicrobial agent reported to inhibit both Gram-positive and Gram-negative bacteria and fungi.14,15Taking into account these results,the susceptibility of methanogenic archaea to antibiotics reflects the phylogenetic position of the archaea as a unique domain of life,different from that of bacteria,eukarya and large DNA viruses.1,2Moreover,the antimicrobial susceptibility data reported herein may help in designing selective media for the isolation of new archaea from diverse environmental and host-associated microbiota.These data further point to the opportunity to develop new families of molecules for the specific inhibition of archaea,especially in light of the potential role of these organisms in animal and human infections.32FundingThis study was funded by URMITE UMR CNRS 6236,Universite ´de la Me ´d-iterrane ´e,France.Transparency declarationsThe co-authors declare that they are the co-inventors of a pending patent on the 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