基督教新教Protestants天主教Catholics东正教Orthodox Christians道教Taoism大乘佛教 Mahayana Buddhism儒家思想Confucianism

“哥特”是指野蛮人。在欧洲人眼里罗马式是正统艺术,继而兴起的新的建筑形式就被贬为“哥特”(野蛮)了。

最早期的基督教只有一个教会,但在基督教的历史进程中却分化为许多宗派,主要有罗马天主教(又称天主教会)、东正教(又称正教会)、新教(又称抗罗宗)三大派别,以及其他一些影响较小的派别。中文语境的“基督教”一词时常是专指新教,这是中文目前的特有现象。
from:http://zh.wikipedia.org/wiki/基督教

Worldwide the three largest groups of Christianity are the Roman Catholic Church, the Eastern Orthodox churches, and the various denominations of Protestantism. The Roman Catholic and Eastern Orthodox patriarchates split from one another in the East–West Schism of 1054 AD, and Protestantism came into existence during the Protestant Reformation of the 16th century, splitting from the Roman Catholic Church. http://en.wikipedia.org/wiki/Christianity
全世界的最大的三个基督教组织是罗马天主教(Roman Catholic Church),东正教(Eastern Orthodox churches)和各种教派的新教(Protestantism)。罗马天主教与东正教的教区在公元1054年东西方宗教大分裂中彼此分裂,新教在16世纪的宗教改革(Protestant Reformation)期间从罗马天主教中分裂而进入存在。

Christianity in China is a growing minority religion that comprises Protestants (Chinese: 基督教; pinyin: Jīdūjiào; literally "Christ Religion" or Chinese: 新教; pinyin: Xīn jiào; literally "New Churches"), Catholics (Chinese: 天主教; pinyin: Tiānzhǔjiào; literally "Lord of Heaven Religion"), and a small number of Orthodox Christians (Chinese: 東正教/东正教; pinyin: Dōngzhèngjiào; literally "Eastern Orthodox Churches"). Although its lineage in China is not as ancient as the institutional religions of Taoism and Mahayana Buddhism, and the social system and ideology of Confucianism, Christianity has existed in China since at least the seventh century and has gained influence over the past 200 years. http://en.wikipedia.org/wiki/基督教
在中国基督教是一个增长中的少数派宗教,包含Protestants新教,Catholics天主教和少量的Orthodox Christians东正教。尽管它在中国的谱系不像制度性的道教和大乘佛教、儒家的社会制度和意识形态一样古老,基督教也已经自从至少7世纪就存在于中国,并且获得影响力在过去的200年。

时间:2012-05-21 上午9:46:00 
标签: 基督教

2014-01-11 20:04:49 Migrated From Blogger

Google地图地理经纬度坐标查询 DMS度分秒MinDec小数分DegDec小数分转换

经纬度坐标
赤道纬度(0°N)
东经正数,西经为负数
北纬为正数,南纬为负数。

通常表示地理坐标系时,前面是纬度后面是经度,
LAT.latitude,纬度
LON.longitude,经度
coordinate坐标

Google地图查看经纬度
地图上点鼠标右键,弹出右键菜单,选择最下面的“这儿是什么?”,即会在输入框中显示当前位置的小数格式坐标,有六位小数,前为纬度后经度。

在线转换经纬度:小数格式经纬度和度数格式经纬度转换
http://www.zhongguosou.com/zonghe/dili_jingweidu.html    @Troy at MSCBSC
其实换算也挺简单,经纬度的度分秒类似于时间的时分秒,比率都是60.

Mimee国外英语版的在线转换工具。
http://80calcs.pagesperso-orange.fr/Downloads/Mimee_online.html
Mimee is a program which can convert geographical coordinates between various datums and formats
D.ddd DegDec,degres decimal 小数度
D.MMmm MinDec,minute decimal 小数分
D.MMSSss DMS,degree minute second 度分秒

Geographic coordinate system
A geographic coordinate system is a coordinate system that enables every location on the Earth to be specified by a set of numbers.A common choice of coordinates is latitude, longitude and elevation.
地理坐标系统是一个能够使地球上第一个位置用一套数字来指定坐标系统。坐标的一般选择是纬度、经度和海拔。
The latitude (abbreviation: Lat., φ, or phi)
The Longitude (abbreviation: Long., λ, or lambda)
from:http://en.wikipedia.org/wiki/Geographic_coordinate_system

There are three basic forms of a coordinate.
Coordinate containing degrees (integer), minutes (integer), and seconds (integer, or real number) (DMS).
Coordinate containing degrees (integer) and minutes (real number) (MinDec).
Coordinate containing only degrees (real number) (DegDec).
All forms of coordinates are capable of representing the same amount of data and the same precision. Depending on which type of coordinate you are provided with, and which type you would like to work with, you may have to do some conversion.
http://en.wikipedia.org/wiki/Geographic_coordinate_conversion
有三种格式的坐标。
1.DMS  包含度(整数)、分(整数)和秒(整数或者实数)的坐标
2.MinDec 包含度(整数)、分(实数)的坐标
3.DegDec 仅包含度(实数)
所有格式的坐标能够代表相同数量的数据和相同的精度。针对你提供的坐标类型和你想要的类型,你需要做一些转换。
Conversion from DMS to Decimal Degree
Conversion from MinDec to Decimal Degree
Conversion from Decimal Degree to DMS

DMS,degree minute second 度分秒
MinDec,minute decimal 小数分
DegDec,degres decimal 小数度

GRS 80, or Geodetic Reference System 1980, is a geodetic reference system consisting of a global reference ellipsoid and a gravity field model.
WGS.World Geodetic System 世界坐标系
GPS所采用的坐标系是美国国防部1984世界坐标系,简称WGS-84。

A latitude of 0°0′0″ is neither North nor South. Similarly, a longitude of 0°0′0″ is neither East nor West. These are referred to as zero latitude or zero longitude.
0度0分0秒纬度,既不是北纬还是南纬。同样地,0度0分0秒经度,既不是东经也不是西经。它们被称作0度经度或0度纬度。

时间:2012-05-20 下午11:02:00 
标签: google, 地图, 坐标

2014-01-10 18:58:08 Migrated From Blogger

blogger网站来源统计中的Referer spam如bestbxcleaner savegco-antivir

在google blogger后台的“统计信息|流量来源”中,经常有看到一些奇怪的站点。
引用的网址:
http://www3.bestbxcleaner.com/?y7i35k=nazSl3KgmJ6nms7roJmXh%2BLZ3rZsmpVqn5abqaeYrIc%3D
http://www4.savegco-antivir.com/?92d7i5=XafNm6ZqqZqqi9PWrF6RpJrd6tWvbGObbKJp15WmlZ%2BH
http://www3.personal-scanera.com/?8sjg=XOjTy62aqKyjlM3faqCVh%2BLZ3p5opNCcoJnWqdOhkZA%3D
http://www4.best-aruchecker.com/?7mlwvblk4=W%2BLV27OXoqRoiNHmsVqTmOnX1KLGnMenmaGfrKuYpY8%3D
http://www3.bestbxcleaner.com/?5d4zd=Wdmd3qGXm6yoiOTWqZKTlNnmoaGXq5yXyqfZmKqUz4k%3D
http://adf.ly/79fa8
http://adf.ly/7AgFq
http://tinyurl.com/Free100USDGoogleAdwords
http://tinyurl.com/Tips100KTwitterFollowers
引用的站点:
www3.bestbxcleaner.com
www4.savegco-antivir.com
www3.personal-scanera.com
www4.best-aruchecker.com
adf.ly
tinyurl.com

在尝试打开这些网址时,基本都失败。搜索也难以找到有用的中文信息。这个问题困惑我好久。我的blogger没什么流量,看起来往往就数它们的流量大。
今天,凭我的三脚猫的英文知识+有道词典,看了些英文资料,主要是英文维基百科和Nitecruzr的blogger(blogging.nitecruzr.net),有了一些粗略的认识。

1.这种手段是一种黑帽SEO(Blackhat SEO)技术。通称Referer spam.
2.它是“垃圾索引Spamdexing”的一种。
Spamdexing有两类,内容垃圾content spam和链接垃圾link spam.
这种奇怪流量来源,是属于Spamdexing中的link spam的一种,叫做“Referrer log spamming(来源记录垃圾信息)”
Referrer log spamming,又叫做Referer spam,log spam or referer bombing
3.这种垃圾来源信息,对于spammer(垃圾信息制造者),可能有两方面的好处。
  3.1如果网站的流量来源统计信息公开,即可以给spammer的网站做反向链接,即可以提高网站的网页排名PR.(PageRank)
  3.2链接指向站点可能会带有木马病毒,使点击者中毒。这点要严重注意!但是否属实,我也不清楚。
4.Referer spam是种错误拼写,长期误用也就将错就错了,正确的是Referrer spam.
5.英文维基的Spamdexing词条说,对Referer spam的一个解决方法是把网站统计不公开。但我觉得似乎这只能是不会提高spammer的站点的PR,而Referer spam照样存在。
6.网站统计日志(Stats logs)中因为Referer Spam显示出的流量和引用站点网页数字,都是虚假的,事实上没有这些引用的网址或网站。
7.Nitecruzr称:google blogger中的自带统计中的这些垃圾链接、来源,只要不去点击就没关系,而所能做的最好的办法,也就是不去点击,暂时还没什么有效的去除方法,因为它们和正常的访问没什么两样。还是就是,通过第三方统计,可以获得准确全面的统计。
详见:http://blogging.nitecruzr.net/2011/11/referer-spam-does-not-represent-real.html
8.英文有限,可能很多理解有偏差,Referer的恰当翻译也没找见。

越发的感觉到,英文好是多么的有优势,在获取信息方面。
虽然我们中文互联网发展很快现在也很庞大,但信息质量与英文互联网相去甚远。
简单来说,如果把英文维基的些词条翻译成中文,做成一个网站,肯定会是一个流量很好的网站。因为很多英文资料,中文并没有对应的信息。但显然,一来这很侵权,二来这个工作量也很庞大。
想来,翻译外文文章是不少人和网站的一个创造有价值的原创中文信息的好方法。
——————————–
When a Web browser user clicks a link from one page to another, the request to the second site includes an HTTP header called the referrer, with the URL of the first page.
到另一个站点的请求包含叫做referrer的HTTP头,包含第一个页面的URL

HTTP Referer二三事
May 5th, 2007 Fwolf
什么是HTTP Referer
简言之,HTTP Referer是header的一部分,当浏览器向web服务器发送请求的时候,一般会带上Referer,告诉服务器我是从哪个页面链接过来的,服务器籍此可以获得一些信息用于处理。比如从我主页上链接到一个朋友那里,他的服务器就能够从HTTP Referer中统计出每天有多少用户点击我主页上的链接访问他的网站。
Referer其实应该是英文单词Referrer,不过拼错的人太多了,所以编写标准的人也就将错就错了。
个人感觉现在Rerferer除了用在防盗链,其他用途最多的就是访问统计,比如统计用户都是从哪里的链接访问过来的等等。
http://www.fwolf.com/blog/post/320

HTTP referrer
HTTP参照位址 (referer,或 HTTP referer),是HTTP表头的一个字段,用来表示从哪儿连结到目前的网页,采用的格式是URL。换句话说,借着HTTP参照位址,目前的网页可以检查访客从哪里而来,这也常被用来对付伪造的跨网站请求。
http://zh.wikipedia.org/wiki/HTTP_referrer

Referer spam
Referer spam (also known as log spam or referer bombing[1]) is a kind of spamdexing (spamming aimed at search engines). The technique involves making repeated web site requests using a fake referer URL that points to the site the spammer wishes to advertise.[2] Sites that publicize their access logs, including referer statistics, will then inadvertently link back to the spammer’s site. These links will be indexed by search engines as they crawl the access logs.
This benefits the spammer because of the free link, which gives the spammer’s site improved search engine ranking due to link-counting algorithms that search engines use.
Technical solutions
As with e-mail spam, web site operators who receive unwanted referer spam may respond using filtering and blocking. A simple attempt at rendering this form of spam ineffective is to prevent the search engine spiders from crawling the site logs by moving them to a non-public area such as a password-protected area, by using a robot exclusion file, or by appending the nofollow value to the links.
http://en.wikipedia.org/wiki/Referer_spam

Spamdexing:Common spamdexing techniques can be classified into two broad classes: content spam[4] (or term spam) and link spam.
Link spam
Referrer log spamming
Referrer spam takes place when a spam perpetrator or facilitator accesses a web page (the referee), by following a link from another web page (the referrer), so that the referee is given the address of the referrer by the person’s Internet browser. Some websites have a referrer log which shows which pages link to that site. By having a robot randomly access many sites enough times, with a message or specific address given as the referrer, that message or Internet address then appears in the referrer log of those sites that have referrer logs. Since some Web search engines base the importance of sites on the number of different sites linking to them, referrer-log spam may increase the search engine rankings of the spammer’s sites. Also, site administrators who notice the referrer log entries in their logs may follow the link back to the spammer’s referrer page.
http://en.wikipedia.org/wiki/Spamdexing#Link_spam

Nitecruzr – Blogger Top Contributor  2012.5月12日
It’s referer spam – and this particular URL may involve active hacking.
Nobody is actually viewing your blog from these sites – and nobody knows about these links but you, since only you can see your Stats logs.  There are no links to your blog, from these websites.
http://productforums.google.com/forum/#!msg/blogger/fOptZd0MMeo/bai88famNn8J
实际上没有人查看你的blog从这些站点,除了你也没有人知道这些链接,因为只有你能够看到你的统计日志。没有从这些站点到你的blog的链接。

jewels2012ascend  2012.5月12日
I have to mention also that the www3 or with the number 3 after the www is LOADED with a Trojan Virus… I know cause I was told by a tech person who is expert in computers. If you click on it, you get the Trojan and it does seep deep down into your computer and very aggressive… Google has got to come up with a way to stop this for folks.
http://productforums.google.com/forum/#!msg/blogger/fOptZd0MMeo/bai88famNn8J

Referer Spam Does Not Represent Real Traffic, To Our Blogs
MONDAY, NOVEMBER 07, 2011
Referer spam simply cannot be blocked, because it is not different from legitimate traffic.
The numbers reflected in our Stats logs do not represent any actual traffic against our blogs, or any websites with links to our blogs. The only person who benefits from referer spam is the owner of the advertised (fake referer URL) sites – and that happens only when we click on the links in the Stats display.
All third party visitor logs and meters, which depend upon snippets or widgets added to the blog template, are not subject to this problem.
So, besides my facetious advice that you simply
Don’t click on the links.
comes equally facetious advice that you
Get a third party visitor log / meter, for accurate and comprehensive pageview counts.
http://blogging.nitecruzr.net/2011/11/referer-spam-does-not-represent-real.html

Bestbxcleaner.com Whois
Registrar
BIZCN.COM, INC.
Whois Server
whois.bizcn.com
Referral URL
http://www.bizcn.com
Creation Date
04/30/2012
Updated Date
04/30/2012
Expiration Date
04/30/2013
Registrant
Dudelange, Lu 3440
cn
Telephone: +35220203602
Fax: +35220203602
Email: benji.rubes@yahoo.com

商务中国(www.bizcn.com)
运营中心地址:厦门软件园(二期)望海路61号 邮编:361008
电话:0592-2577888 传真:0592-5724400

———————
黑帽SEO:所有使用作弊手段或可疑手段的,都可以称为黑帽SEO。
黑帽SEO与白帽SEO对比            Blackhat SEO
站在黑帽SEO的角度,他们也有他们的道理。因为大部分黑帽SEO都是使用程序,他们建立一个几万几十万页的网页,不费吹灰之力,只要放他们的蜘蛛出去抓取就可以了。就算过几个月他们的网站被惩罚,他可能已经赚了几千几万美金了。对他来说,投资报酬率还是相当高的。
站在白帽SEO的立场上,这种放长线掉大鱼的策略,即使很正确,有的人也不愿意这么做。认真建设一个网站,有的时候是一件很无聊的事。你要写内容,要做调查,要做分析流量,要分析用户浏览路径,要和用户交流沟通。
黑帽SEO要做的就简单多了。买个域名,甚至可以就使用免费虚拟主机,连域名都省了。程序一打开,放上Adsense编码,到其他留言本或博客留一些言(这些留言也有可能是程序自动生成的),然后就等着收支票了。
黑帽SEO的正面意义
1. 变换着手法,在不同程度的拿案例实践着,为SEO提供了很多指导价值。
2. 不断的试探着搜索引擎的底线,没有他们的实验,白帽SEO也很难有所提升,危险性也大。
3. 相比搜索引擎优化是一门艺术,黑帽SEO更算得上是了。
http://baike.baidu.com/view/1064169.htm

时间:2012-05-14 下午10:07:00 
标签: blogger, 病毒, 英文

2014-01-07 16:54:36 Migrated From Blogger

统计statistics的缩写Stats

在The Real Blogger Status中看关于Referer Spam的posts,看到有Stats,在有道词典桌面版中查询,只是查到有个“abbr. 静止坦克自动目标系统(Stationary Tank Automatic Target System)”
起初还当是作者笔误,把status写成了stats.后来看到有很多次出现,又搜索了下,才知道原来是统计statistics的缩写。

我以前对缩写词挺有兴致,看并记过很多缩写,居然印象中从没见过这个缩写,较奇怪。

stats 缩写词 abbr. =statistics
statistics 美音:[stə’tɪstɪks] 统计,统计资料,统计学
http://dict.baidu.com/s?wd=stats

时间:2012-05-14 上午10:45:00 
标签: 缩写, 英语

2014-01-07 16:45:46 Migrated From Blogger

论文翻译Water uptake by barley roots as affected by the osmotic and matric potential in the rhizosphere根际中大麦根系吸收水分受渗透和基质势人影响

Water uptake by barley roots as affected by the osmotic and matric potential in the rhizosphere

Biomedical and Life Sciences Plant and Soil
Volume 94, Number 1, 143-146, DOI: 10.1007/BF02380596
U. Schleiff

Google 翻译

http://translate.google.com.tw/#
————————————–
Bad translation by xuexx at 110310

植物和土壤94,143-146(1986)                 Ms. 6080
9 1986 Martinus Ni/hoffPublishers, Dordrecht 在荷兰出版。

根际中大麦根系吸收水分受渗透和基质势人影响
U. SCHLEIFF
ETH-Zi~rich Department of Crop Science, CH-830 7 Eschikon-Lindau, 瑞士
1985年8月30日收到。1985年12月修订。
关键词 大麦 根际 耐盐性 土壤水势

摘要
盐碱土中根系对水的吸收率受到抑制的同时,根系周围土壤基质势和渗透水势也降低。遗憾的是,没有可靠的工具,可用于直接测量根际土壤中根的水吸收率降低的效果。本文展示了不同水势和基质势组合对根际土壤中大麦根系水吸收率的影响一些植物实验的结果。

降低土壤基质水势比起降低土壤渗透水势,使水吸收率降低到一个更大的程度。根据本实验的结果,砂土的总水势和当根系处在不同的基质势和渗透势时的水吸

简介
当根系对水分的吸收发生在盐碱土中时,近根系土壤水势下降更多,比起远离根系土壤。因此,在水耗尽期,根暴露在土壤基质势和水势,本质上不同于大块土壤。为了提高我们对生长在盐碱土中作物的水供应过程的理解,减少在根周围土壤渗透基质水势不得不定量地决定。
从各个田野和盆栽试验,得出的结论是,在一般情况下,相等的降低渗透和基质土壤水势对影响水供应和作物生长有一人相似的程度。因为作物抵抗土壤盐碱度和渗透胁迫的能力显著不同,这是众所周知,这个概念可能不适用所有作物。一些耐盐碱作物例如甜菜和大麦可以调整他们面子水势应对渗透胁迫,因此,渗透性土壤水分胁迫比起基质土壤水分胁迫对它们的水供应较少影响。基于这个假设这个实验的目的就是研究根系在不同的总土壤水势下从土壤中的水分吸收情况。

材料和方法
生长在一升的装有轻质土壤(370g黄土和1230g沙子的混合)盆的大麦植株。盆有 盖子覆盖,盖上有一个为了幼苗刺穿的小洞。盆的水容量是体积的20%。植物生长周期共分为两个阶段,最初栽培期36天,随后的实验阶段用4天(表1)。最初的栽培阶段是为了获得有茂密根系的良好的成年植株。被选择盐碱化处理的植物,被适应于加入10mmol/l氯化钠到水中的含盐生长环境,用于在最初的栽培期灌溉植物。被选择研究降低土壤基质势的影响的植株,不接受氯化钠。在在初始阶段结束时,由于土壤含水量下降到了3-4%,对应的土壤基质势0.1- 0.15兆帕,所有的植物枯萎。植物枯萎发生在相对高基质势中,因为植物暴露到干旱的生长环境中(30-35~29-40%空气相对温度),根密度是极端高(~15cm/cm^3).芽重量是1.4+-0.1g DM/shoot ,根重量1.0*0.1g DM/根(5盆平均数)

表1.
不同处理的氯化钠添加量在最初栽培期和处理期

实验期的目的是为了测量大麦根系暴露到不同渗透和基质土壤水势的根际土壤中时的水分吸收率。因此这个实验期开始靠用不同盐浓度(表1)150ml水/盆灌溉植株接近盆容量.灌溉3小时盆重被确定,植株暴露到模拟上面描述的干旱环境中。在接着的4天水消耗期间,土壤水损失(蒸发土壤水)由几次盆称重值决定。土壤基质和渗透水势被计算从土壤水容量。土壤的pF曲线靠暴露样品到相应的吸力而获得,较低的值被应用相应的压力。附加实验详情已经被报告。

结果和讨论
a)土壤水分状况的过程
相关的一些具有代表性的盆的土壤水势过程观测将被提交。在实验的开始(fig.1,0h),所有盆的土壤基质水势是0.01Mpa ,土壤水容量大约15%。土壤溶液浓度不同导致在土壤渗透和总水势排列从水势0.01Mpa到1.0Mpa的不同。
在随后的水消耗期,土壤水势的显著不同被观察到。在非盐碱对照处理的土壤水容量下降到4%,在照明25小时后,相当于基质势的值为0.06Mpa.到实验结束时,土壤基质势的值达到0.3Mpa ,这将引起植株严重的萎蔫。
在用包含25mmol氯化钠/升的水灌溉盆时,土壤基质水势过程概念股最初25小时的照明相似。到实验结束时,基质势的值大约达到0.2Mpa.由于在最初栽培中,这个处理的土壤被轻微地盐碱化,更多的盐将被加入以灌溉水,植株已经被暴露到土壤的全水势,在实验开始的0.5Mpa。在接着的25h,the ~kT-value降低到大约1.2Mpa,主要是由于增加的土壤溶液盐浓度。在实验末,the ~T-Value大约是3.0Mpa,其中2.8Mpa是渗透势,仅仅有0.2Mpa是基质势。

b)根的水吸收
根的水吸收率的计算是基于1gDM形成一个长有150m的根的一个根土的假设。在实验期间根密度的增加被认为是不重要的对于水吸收,因此,不予考虑。
在水消耗期,土壤水势增加反过来影响根的水分吸收率。fig2展示了土壤fiT和暴露于非盐碱土壤和两个盐碱土壤的根的水分吸收率的关系。在第一个水消耗期(0-11小时)的平均的水吸收率改变在无盐碱的2.1 ,低盐碱的2.3和高盐碱的1.7.它是明显的,非常相似的吸收率发生在在非盐碱和低盐碱的处理的土壤中,本质上不同于他们的总水势。这些土壤T-Values的不同是唯一地被他们的滲透势值的不同所引起,然而基质势值是高的。显然,土壤渗透势对于根系水分吸收是较低重要性的。
在第二个照明期间(11-25小时),水分吸收率趋向更高比在第一时期,因为在温室中的空气温度是更高了。最高的平均水吸收率3.3是被发现在非盐碱盆,在土壤t值减少从15kpa到60kpa.在低盐碱盆中,水吸收率轻变低,然而t值的减少是显著的(从0.7到1.2Mpa).最低的水吸收率1.5被观察到了在高盐碱环境,在那,t值减小从1.2到1.5Mpa.这些数据也显示土壤t值对于描述植物水供应不是今人满意的标准。在第三个照明期,水吸收率的对比也显示出了在1.1到1.3时相似的吸收率发生在非常不同的土壤水势中。
这些结果是相对于其他作者的发现,那些发现在作物中相似的水供应减少人,在减少的土壤的t值,t值独立的组件。几个原因能解释这些不同的结果。在这个实验中,一个耐受盐的作物被选择,它能够达到大的程度,来补偿在根际的渗透胁迫。其它的作者曾经选择豆子、柑橘和苜蓿,它们有较小的耐盐性。另一个原因可能是土壤的纹理与非常多的根结合在实验中。砂土包含很少的水,基质势0.1Mpa,甚至更低。相同程度渗透势的值能够被在盐碱和砂土中达到相对高土壤水分,但许多植物水分吸收因此轻微降低。
在这个实验中,水分吸收中基质势的值的作用可能是更引人注目的,由于高的根密度,根际基质势唯一地被测量,而非土壤层的基质势的平均值。这意味着植物供水不能靠来处外界根际和根生长进入非根际土壤的水通量提高。

总结本次实验的结果,土壤渗透和基质水势成分影响所有作物水分吸收到相同的程度,这是今人怀疑的。

————-
original text
http://www.springerlink.com/content/b36244880520810x/

Plant and Soil 94,143-146 (1986).
9 1986 Martinus Ni/hoffPublishers, Dordrecht. Printed in the Netherlands.
Ms. 6080
Water uptake by barley roots as affected by the osmotic and
matric potential in the rhizosphere
U. SCHLEIFF
ETH-Zi~rich Department of Crop Science, CH-830 7 Eschikon-Lindau, Switzerland
Received 30 August 1985. Revised December 1985.
Key words Barley Rhizosphere Salt tolerance Soil water potential
Summary The water uptake rates of roots in saline soils are depressed by the simultaneously
decreasing matric (r and osmotic (~o) water potentials in the soil surrounding the roots
(rhizospheric soil). Unfortunately there are no reliable tools available for direct measurements
of the effect of decreasing water potentials in the rhizospheric soil on the uptake rate of soil
water by roots. This paper presents some results of a vegetation technique for studying the
effect of different combinations of osmotic and matric water potentials in the rhizospheric
soil on the water uptake rates of barley roots.
Water uptake rates were reduced to a greater extent by decreasing soil matric water potentials
than by decreasing soil osmotic water potentials. According to the results of this experiment,
there was no relationship between the total soil water potential (r of a sandy soil
and the water uptake rates when the roots were exposed to different combinations of ~M and
fro-
Introduction
When water uptake by roots occurs in saline soils, the water potential of the soil near the
roots (rhizospheric soil) drops much more than in the soil further away from the roots. Thus,
during a period of water depletion roots can be exposed to soil osmotic and matric water
potentials that differ essentially from the bulk soil. In order to improve our understanding
of the processes of water supply to crops growing in saline soils, the effects of decreasing
osmotic and matric water potentials in the soil surrounding the roots have to be determined
quantitatively.
From various field and pot experiments, it was concluded that, in general, equivalent
decreases in osmotic and matric soil water potentials affect the water supply and the growth
of crops to a similar degree 2,3,4’5’8’9. Since it is well-known that crops differ significantly
in their ability to overcome soil salinity resp. osmotic stress, this concept might not be applicable
to all crops. Some salt tolerant crops such as sugar beets and barley may adapt their
leaf water potentials to osmotic stress and therefore their water supply should be less affected
by osmotic soil water stress than by matric soil water stress. Based on this assumption it was
the aim of this experiment to study the root water uptake from a soil with various combinations
of the total soil water potentials.
Materials and methods
Barley plants (one plant/pot, cv. Aura) were grown in l-liter pots filled with a light-textured
soil (mixture of 370g loess and 1230g sand). The pots were covered with a lid, in which a
small hole had been pierced for the seedling. The water capacity of the pots was 20 Vol.%.
The total growth period of the plants was divided into two periods, an initial cultivation
143
144 SHORT COMMUNICATION
phase of 36 days and a succeeding experimental phase of 4 days (Table 1). The aim of the
initial phase of cultivation was to obtain well grown plants having a dense root system. Plants
selected for salinization treatments were adapted to saline growth conditions by adding 10 mmol
NaC1/I to the water and used for irrigating the plants during the initial phase of cultivation.
Plants selected for studying the effect of decreasing soil matric potential did not received NaCI.
At the end of the initial phase, all plants were wilting due to a drop in soil water content to
3-4 Vol.% corresponding to a soil matric potential of–0.1 to –0.15 MPa. The wilting of the
plants occurred at these relatively high matric potentials since the plants were exposed to arid
growth conditions (30-35~ 29-40% relative air humidity) and the density of the roots was
extremely high (~ 15 cm/cm3). The shoot weight was 1.4 -+ 0.1 g DM/shoot and the root weight
1.0 x 0.1 g DM/root (average of 5 pots).
Table 1. Sodium chloride additions (mmol/pot) to the various treatments during the initial
phase of cultivation and during the treatment phase
Treatments (mmol NaC1/pot)
NaCl-conc. of water
(retool~l) Non saline 0 25 150 300 450
Initial phase
of cultivation 0 8 8 8 8 8
Treatment phase 0 0 3.75 22.5 45 67.5
Total 0 8 11.75 30.5 53 75.5
The aim of the experimental phase was to measure the water uptake rates of barley roots
exposed to a rhizospheric soil with different combinations of osmotic and matric soil water
potentials. The experimental phase was therefore begun by irrigating the plants near to pot
capacity with 150ml/pot water of different salt concentrations (Table 1). Three hours after
irrigation the pot weight was determined and the plants exposed to simulated aridity as described
above. During the following 4 days period of water depletion, the water losses of the
soil (= transpired soil water) were determined by weighing the pots several times. The matric
and osmotic water potentials of the soils were calculated from the soil water contents. The
pF-curve of the soil was obtained by exposing the samples to a corresponding suction, the
lower values (–80 to –1500kPa) by applying corresponding pressures. Additional experimental
details have already been reported 7.
Results and discussion
a) Course of the soil water status
Observations related to the course of the soil water potential in a few representative pots
will be presented. At the beginning of the experiment (Fig. 1, 0 h), the soil matric water potential
of all pots was –0.01 MPa at a soil water content around 15 Vol.%. Differences in the salt
concentrations of the soil solutions resulted in great differences in the osmotic and total water
potentials of the soil ranging from total water potentials of– 0.01 MPa to — 1.0 MPa.
During the succeeding periods of water depletion significant differences in the course of the
soil water potentials were observed. The soil water content in the nonsaline treatment dropped
after 25 hours of illumination to about 4 Vol.%, which corresponds to a ~PM-value of –0.06 MPa.
By the end of the experiment, the ~M-value of the soil had reached –0.3 MPa which caused
severe wilting of the plants.
In the pot irrigated with water containing 25 mmol NaC1/1, the course of the soil matrix
water potential was very similar during the first 25 h of illumination. By the end of the experiment,
a ~M-Value of about–0.2MPa had been reached. As the soil of this treatment was
slightly salinized during the initial phase of cultivation and further salts were added with the
irrigation water, the plants had already been exposed to a total water potential of the soil
(r of –0.5 MPa at the beginning of the experiment. During the following 25 h, the ~kT-value
SHORT COMMUNICATION 145
decreased to about –1.2 MPa, mainly due to the increasing salt concentration of the soil
solution. At the end of the experiment the ~T-Value was about–3.0 MPa,- 2.8 MPa of which
were osmotic and only –0.2 MPa were matric potential.
In the high saline treatment (150mmol NaCl/1), the drop in the ffM-value of the soil was
significantly lower. Following an illumination period of 25 h, the ~M-value was –0.02 MPa
which was significantly higher than in the nonsaline and lowsaline treatments. As the water
uptake rates of the plants were significantly reduced, the ffM-value had dropped to about
only — 0.04 MPa by the end of the experiment. Due to the salts dissolved in the soil solution,
the ~0T-Value of this soil had already reached — 1.0 MPa at the beginning of the experiment,
dropped to — 1.5 MPa 25 h later and reached — 2.5 MPa by the end of the experiment.
b) Water uptake by roots
The calculation of the water uptake rates by the roots is based on the assumption that a
root mass of 1 g DM forms a root length of 150 m 6, An increase in the rooting density during
the experimental phase was supposed to be of little importance for the water uptake and,
therefore, not taken into account.
During a period of water depletion, the water potential of the soil decreases which in turn
affects the water uptake rate of roots. Fig. 2 shows the relationship between fiT of the soil and
-o,o, 4 /
-qo2
-qo3
-~176 \ -q30L~ ‘ ~”‘– ~
0
irrigation water :
2×5 15xOmeq NoCI/I
\ \ I: 1
\ \1
[Val.*l.]
-15
– ,2,s
8
-7,s _~
-2s ~n
, tl , , , -0
-q2 -0.4-0.5 -10 -15 -2’0 -2; -3′.0 [MPG]
total water potential at soil
Fig. 1. Relationship between decreasing soil water (due to water depletion by roots) and total
water potential of the rhizospheric soil at various salinity levels.
cm r~t.10h J
saline
5 _~-
1-
o .0.’2 .; .& _o’.~ .,; .,.? .,; .,; _,:~ -2’otMPo] g
total soil water potential
Fig. 2. Water uptake rates of barley roots in relation to the decreasing water potential of the
rhizospheric soil due to root water uptake at different salinity levels.
illumi~lion inle~ol:
x 0 tO llh
25 rnt:~zI I~k3CI/I irrig waler 9 11 10 25h
9 ?25 tO 39h
S o 39 lo 53 h
146 SHORT COMMUNICATION
the water uptake rates of the roots exposed to a nonsaline soil and two salinized soils. The
average water uptake rates during the first water depletion period (0-11 h) varied between
2.1 ~1 in the nonsaline, 2.3 t~l in the lowsaline and 1.7 ~l/cm root. 10 h in the highsaline treatment.
It is obvious that the very similar uptake rates in the nonsaline and low saline treatments
occurred in soils differing essentially in their total water potentials. The differences in the
~/T-Values of these soils were exclusively caused by differences in their Co-values, whereas the
CM-Values were high (> — 0.015 MPa). Obviously the soil osmotic potential was of low importance
for the water uptake by the root system.
During the second illumination interval (11-25 h), the water uptake rates tended to be
higher than during the first period since the air temperature in the greenhouse was higher.
The highest average water uptake rate of 3.3#1 was found in the nonsaline pot at a ~T-Value of
the soil decreasing from — 15 kPa to –60 kPa. In the lowsaline pot the water uptake rate was
slightly lower (2.7~1/cm root. 10h), whereas the decrease in the ,VT-Value was significant
(from –0.7 to –1.2 MPa). The lowest water uptake rate of 1.5 ~1 was observed in the highly
saline soil in which the CT-Value decreased from — 1.2 to — 1.5 MPa. These data show too that
the CT-Values of the soils were unsatisfactory criteria for characterizing the water supply to
the plants. The comparison of the water uptake rates during the third period of illumination
shows also that very similar uptake rates of 1.1 to 1.3 ul occurred in soils of very different soil
water potentials (~T from –0.1 MPa to — 1.6 MPa).
These results are in contrast to the findings of other authors 3’s’9, who found similar reductions
in crop water supply at decreasing CT-Values of the soil, independent of the components
of the qJT-Value. Several reasons could be responsible for these different results. In this
experiment, a salt tolerant crop was chosen, which was able, to a great extent, to compensate
for the osmotic stress in the rhizosphere. The other authors had selected beans, citrus and
alfalfa, which are less salt tolerant. Another reason could have been the texture of the soil
in combination with the extremely high rooting density in this experiment. A sandy soil contains
little water at a r of- 0.1 MPa or even lower. A ~0 o-value of the same degree can
be reached in a saline, sandy soil at relatively high soil water contents, but the water uptake of
many plants is thereby reduced only slightly.
The effect of lower qJM-Values on the water uptake may have been more dramatic in this
experiment as, due to the high rooting density, the qJM-Value of the rhizosphere exclusively was
measured and not the qJM-Value of a soil layer in average. This means that the water supply
of the plants could not be improved by a water flux from outside the rhizosphere and by roots
growing into nonrhizospheric soil.
In summarizing the results of this experiment, it is doubtful that the osmotic and matric
component of the soil water potential affect the water uptake of all crops to the same degree.
References
1 Ayers R S and Westcot D W 1976 Water Quality for Agriculture. FAO, Rome, p. 20.
2 Bresler E, McNeal B L and Carter D L 1982 Saline and sodic soils. Advanced series in
agricultural sciences 10, Springer, Berlin-Heidelberg-New York, 139-43.
3 Dirksen C 1985 Irrig. Sci. 6, 39-50.
4 HanksRJetal. 1978 Irrig. Sci. 1,47.
5 Plessis du H M 1985 Irrig. Sci. 6, 51-61.
6 Russell R S 1977 Plant root systems – their Function and Interaction with the Soil.
McGraw-Hill Book Company (UK) Limited, London, pp 9-29.
7 Schleiff U 1983 lrrig. Sci. 4,177-189.
8 Wadleigh C H and Ayers R S 1945 Plant Physiol. 20,106-132.
9 Wadleigh C H 1946 Soil Sci. 61,225-38.