My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
9597
CWCB
>
UCREFRP
>
Public
>
9597
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
7/14/2009 5:02:36 PM
Creation date
5/20/2009 3:01:13 PM
Metadata
Fields
Template:
UCREFRP
UCREFRP Catalog Number
9597
Author
U.S. Environmental Protection Agency.
Title
Biological Field and Laboratory Methods for Measuring the Quality of Surface Waters and Effluents.
USFW Year
1973.
USFW - Doc Type
Cincinnati, OH.
Copyright Material
NO
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
195
PDF
Print
Pages to print
Enter page numbers and/or page ranges separated by commas. For example, 1,3,5-12.
After downloading, print the document using a PDF reader (e.g. Adobe Reader).
Show annotations
View images
View plain text
<br />. <br /> <br />X 2 is computed as <br />_ 2: (0 ij- Eij)2 <br />X2 -.. E" - 2.69(n.s.) <br />I] IJ <br /> <br />F or this type of hypothesis, there are (rows - 1) <br />(colums - 1) degrees of freedom, in this case <br />(3) (2) = 6 <br /> <br />In the example, X2 is nonsignificant. Thus, there <br />is no evidence that the ratios among the organ- <br />isms are different for different streams. <br /> <br />Tests of two types of hypotheses by X2 have <br />been illustrated. The first type of hypothesis was <br />one where there was a theoretical ratio, i.e., the <br />ratio of males to females is 1: 1. The second type <br />of hypothesis was one where equal ratios were <br />hypothesized, but the values of the ratios <br />themselves were computed from the data. To <br />draw the proper inference, it is important to <br />make a distinction between these two types of <br />hypotheses. Because the ratios are derived from <br />the data in the later case, a better fit to these <br />ratios (smaller X2) is expected. This is compen- <br />sated for by loss of degrees of freedom. Thus, <br />smaller computed X2's may be judged signifi- <br />cant than would be in the case where the ratios <br />are hypothesized independently of the data. <br /> <br />5.3 F-test <br /> <br />The F distribution is used for testing equality <br />of variance. Values of F are found in books of <br />mathematical and statistical tables as well as in <br />most statistics texts. Computation of the F <br />statistic involves the ratio of two variances, each <br />with associated degrees of freedom. Both of <br />these are used to enter the table. At any entry of <br />the F tables for (nl - 1) and (n2 - 1) degrees of <br />freedom, there are usually two or more entries. <br />These entries are for various levels of probability <br />of rejection of the null hypothesis when in fact <br />it is true. <br />The simplest F may be computed by forming <br />the ratio of two variances. The null hypothesis is <br />~ : a12 = a2 2. The F statistic is <br />Sl2 <br />F=- <br />S22 <br /> <br />(36) <br /> <br />. <br /> <br />where S12 is computed from nl observations <br />and S22 from n2' For simple variances, the <br />degrees of freedom, f, will be f1 = n1 - I and <br /> <br />BIOMETRICS - F-TEST <br /> <br />f2 = n2 - 1. The table is entered at the chosen <br />probability level, a, and if F exceeds the tabu- <br />lated value, it is said that there is a 1 - a <br />probability that al 2 exceeds a2 2. <br /> <br />5.4 Analysis of Variance <br /> <br />Two simple but potentially useful examples <br />of the analysis of variance are presented to <br />illustrate the use of this technique. The analysis <br />of variance is a powerful and general technique <br />applicable to data from virtually any experimen- <br />tal or field study. There are restrictions, however, <br />in the use of the technique. Experimental errors <br />are assumed to be normally (or approximately <br />normally) distributed about a mean of zero and <br />have a common variance; they are also assumed <br />to be independent (i.e., there should be no cor- <br />relations among responses that are unaccounted <br />for by the identifiable factors of the study or by <br />the model). The effects tested must be assumed <br />to be linearly additive. In practice these assump- <br />tions are rarely completely fulfilled, but the <br />analysis of variance can be used unless signifi- <br />cant departures from normality, or correlations <br />among adjacent observations, or other types of <br />measurement bias are suspected. It would be <br />prudent, however, to check with a statistician <br />regarding any uncertainties about the appli- <br />cability of the test before issuing final reports or <br />publications. <br /> <br />5.4.1 Randomized design <br /> <br />The analysis of variance for completely <br />randomized designs provides a technique often <br />useful in field studies. This test is commonly <br />used for data derived from highly-controlled <br />laboratory or field experiments where treat- <br />ments are applied randomly to all experimental <br />units, and the interest lies in whether or not the <br />treatments significantly affected the response of <br />the experimental units. This case may be of use <br />in water quality studies, but in these studies the <br />treatments are the conditions found, or are <br />classifications based upon ecological criteria. <br />Here the desire is to detect any differences in <br />some type of measurement that might exist in <br />conjunction with the field situation or the <br />classifications or criteria. <br />For example, suppose it is desired to test <br />whether the biomass of organisms attaching to <br /> <br />15 <br />
The URL can be used to link to this page
Your browser does not support the video tag.