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. 2024 Sep 23;14(9):e70275. doi: 10.1002/ece3.70275

Diversity analysis: Richness versus evenness

Tarald O Kvålseth 1,
PMCID: PMC11420109  PMID: 39318531

Abstract

Richness and evenness, two important components of diversity, have been the subject of numerous studies exploring their potential dependence or lack thereof. The results have been contradictory and inconclusive, but tending to indicate only a low (positive or negative) correlation. While such reported studies have been based on particular data sets and species abundance distributions, the present article provides the results of a study using randomly generated abundance distributions and hence more generalizable findings and valid statistical results. The results reveal no statistically significant correlation between richness and evenness based on such random sample of abundance distributions and on four well‐known measures of diversity, including Simpson's indices and the entropy index. Of the two diversity components, evenness is found to have the strongest influence on diversity, but for numbers‐equivalent or effective‐number formulations, richness tends to be the most influential diversity component. For analyzing the tradeoff between richness and evenness for any given diversity measure and abundance distribution, the richness‐evenness curve is introduced as a new tool for diversity analysis.

Keywords: biodiversity, diversity, evenness, richness, value validity


Richness and evenness are two important components of any measure of diversity. This article presents a simple graphical method showing the tradeoff between those two components of a diversity measure. Real biological data are used as an illustration.

graphic file with name ECE3-14-e70275-g002.jpg

1. INTRODUCTION

Diversity is generally considered to consist of two components: richness and evenness. In biology and ecology, richness typically means the number of different species in a sample or population while evenness refers to the extent to which the different species are equally represented in the sample (population). Diversity increases as the number of species increases and as their relative proportions become increasingly equal or uniform. As stated by Magurran (2004, p. 9), “Species richness is simply the number of species in the unit of study” while “evenness describes the variability in species abundances.” A diversity index or measure is a statistic that incorporates information about both richness and evenness.

For a sample, collection, or unit of study with a relative abundance distribution Pn=p1p2pn where pi is the proportion (sample probability) of the i‐th species and all pi's sum to 1 (i.e., i=1npi=1), the species richness is simply defined as n. The species evenness refers to how evenly (uniformly) the pi's are distributed, but its measurement is not so simple and remains unsettled (see, for example, Kvålseth, 2015; Smith & Wilson, 1996). With diversity being considered a combination of richness and evenness, a wide variety of diversity indices have been proposed over the years (e.g., Daly et al., 2018; Magurran, 2004, ch. 4–5). In spite of such a variety of ways to measure and interpret diversity, it certainly would be informative to explore whether any kind of relationship exists between the richness and evenness components. Such information could provide for a better understanding of diversity as a concept and of its measurement.

In fact, the relationship between richness and evenness, if any, has been the subject of considerable interest, controversy, and numerous studies and publications. Some have emphasized that richness and evenness should be independent components (e.g., Heip, 1974; Peet, 1974: Smith & Wilson, 1996) while Jost (2010) has argued that they cannot possibly be independent. Others have studied the potential richness‐evenness relationship and generally found limited interaction or low correlations between evenness and richness (e.g., Blowes et al., 2022; Bock et al., 2007; Buzas & Hayek, 2005; Gosselin, 2006; Liu et al., 2023; Ma, 2005; Stirling & Wilsey, 2001; Yan et al., 2023; Zhang et al., 2012). Soininen et al. (2012) conducted a meta‐analysis of various studies and found that “significant correlations of species richness and evenness only existed in 71 out of 229 datasets. Eighty‐nine were negative and 140 were positive (p. 803).” In a study by Su (2018), the indication is that any richness‐evenness relationship will depend on the form of the relative abundance distribution.

The various reported studies exploring a potential relationship between richness and evenness have been based on data collected from particular ecological systems and sites. Ma (2005), for example, studied plant species in different field quadrats in Finland as basis for relative abundance distributions. As another example, Su (2018) used sample data for island birds, stream fishes, and zooplankton in specific locations. In all of these studies, not only did the richness and evenness components vary, but the values of the diversity indices also varied. Another complicating factor in understanding the relationship between richness and evenness is that different measures of diversity and of evenness were used in different studies.

Although the results from individual studies of a potential richness‐evenness relationship or dependence are restricted to the particular ecological systems and species abundance distributions, some generalization may be possible because of the substantial overall reported data sets from varying ecological environments. The meta‐analysis by Soininen et al. (2012) was one such attempt at a generalization with no consistent result, but rather a mixture of negative, positive, or insignificant correlations between richness and evenness. Such lack of consistent results or association between richness and evenness as diversity components also highlights the important point that the frequently used richness by itself is an incomplete measure of diversity.

One way to use a more general data base than those based on particular ecological systems for exploring potential richness‐evenness relationships is the use of randomly generated relative abundance distributions Pn=p1pn where the richness n and each pii=1n are obtained by random number generation. Random sample data can then be used, for example, to test whether any statistically significant correlation exists between richness and evenness. This approach is one of the objectives of the present article. Such random sample data will also be used to assess the potential associations between different diversity measures and between different evenness measures.

Another objective of this article is to determine analytically the relative effects of richness versus evenness on the values of specific diversity measures. Four well‐known diversity measures will be considered, including Simpson's index and the entropy index.

Besides analyses of potential relationships between richness and evenness based on data for which diversity is also a variable, a further objective of this article is to present a method for considering the richness‐evenness relationship for fixed diversity. With richness and evenness being components of diversity, one could consider the tradeoff between those two components for any given value of the diversity. Thus, for any given relative abundance distribution Pn=p1pn and some diversity index with the value DPn, one could consider other distributions Pm with the same diversity value, that is, DPn=DPm, but with different richness mn and different evenness.

Such richness‐evenness tradeoff relationships or graphical curves for fixed diversity will necessarily depend on the diversity measure being used as will be exemplified and illustrated in this article. Although intuitively rather simple to comprehend as a general concept, rigorous analysis and description of the relationship between richness and evenness for a given value of a diversity measure will require some mathematical formulations. Those developments will also emphasize the validity of the formulations. Real biological data will be used as numerical examples.

2. DIVERSITY, RICHNESS, AND EVENNESS

2.1. Definitions

In the most general terms, consider the case of n mutually exclusive and exhaustive categories with the respective probabilities or proportions p1,p2,,pn with each pi0 and i=1npi=1. In biology or ecology, Pn=p1pn becomes the abundance distribution for n different species, with n typically being referred to as the species richness. For a generic diversity measure D, the value EPn of the corresponding evenness index E for the distribution Pn can be defined as the following normalized form of D (Kvålseth, 2015):

EPn=D*Pn=DPnDPn0DPn1DPn00,1 (1)

involving the degenerate and uniform distributions.

Pn0=1,0,,0,Pn1=1/n1/n (2)

The term DPn1 in (1) becomes a function of the richness n.

In its most general form, the diversity value DPn as a function of D*Pn and n can be expressed from (1) as

DPn=DPn1DPn0D*Pn+DPn0 (3)

For the apparently most popular diversity indices, (3) reduces to the following expressions: for Simpson's index (Simpson, 1949),

DSPn=1i=1npi2=11/nDS*Pn (4)

for the entropy due to Shannon (1948),

HPn=i=1npilogpi=lognH*Pn (5)

for the second form of Simpson's index,

DS2Pn=i=1npi21=n1DS2*Pn+1 (6)

and, for the exponential form of the entropy in (5), apparently first proposed by Sheldon (1969),

H2Pn=expHPn=n1H2*Pn+1 (7)

While the above expressions involve the general distribution Pn=p1pn, another special distribution that will be useful in the subsequent analysis is the lambda distribution introduced by Kvålseth (2011) and defined as follows:

Pnλ=1λ+λnλnλn,λ0,1 (8)

where λ is an evenness parameter. This Pnλ is a so‐called mixture distribution, being the weighted mean of the extreme distributions Pn0 and Pn1 in (2), that is,

Pnλ=1λPn0+λPn1 (9)

For the analysis of some diversity index D, the utility of Pnλ comes from the fact that for any Pn,

DPn=DPnλforauniqueλ (10)

as exemplified next.

In terms of the notation used in this article, it should be noted that the strictly mathematically correct notation would be to use D to denote a diversity function and DPn to denote its value for the distribution Pn as used above. However, for the sake of simplicity and where there is no chance of ambiguity, D may sometimes be used both as a function and its numerical value. The same comment applies to other summary measures used in the article.

2.2. Value validity

For any measure of evenness, as with summary measures in general, it is essential that all values of a measure provide true, realistic, or valid representations of the attribute being measured, that is, the evenness characteristic. The conditions for such value‐validity property, first introduced by Kvålseth (2014), have been discussed in detail for evenness indices by Kvålseth (2015).

As a brief outline here, the value‐validity condition for the normalized diversity index D* as a measure of evenness can be derived as follows. Consider first the distribution Pnλ in (8) and its extreme members in (2) as points (vectors) in n‐dimensional Euclidean space, with D*Pn0=0 and D*Pn1=1. Then, in terms of the Euclidean distance function d, the evenness parameter λ can be expressed in terms of metric distances as follows:

d*Pnλ=dPn0Pn1dPnλPn1dPn0Pn1=λ (11)

where dPn0Pn1=maxPnλdPnλPn1. That is, λ equals the relative extent to which the Euclidean distance between Pnλ and Pn1 is less than its maximum distance. The value‐validity condition on the diversity D requires that

D*Pnλ=d*Pnλ=λ (12)

or as an approximation. For the general distribution Pn=p1pn and from (10), the condition in (12) becomes

D*Pn=d*Pn (13)

or approximately so, with Pn substituted for Pnλ in (11).

Therefore, according to (12) and (13), D*Pnλ and D*Pn measure the relative proximity of Pnλ and Pn to the complete evenness distribution Pn1 based on Euclidean distances. For example, for the simple distribution P21/2=0.75,0.25=12P20+12P21, (12) requires that D*P21/2=1/2, which is clearly a most logical result. Nevertheless, none of the diversity indices in (4)–(7) satisfies this condition (Kvålseth, 2015). However, as discussed below, those indices can be corrected so as to comply.

3. RANDOM SAMPLE RESULTS

The wide variety of reported biological studies of the potential relationships between richness and evenness have involved various types of species and environments. Consequently, the results from such studies apply to those specific situations and may not be generalizable to other situations. In order to explore some more general data, distributions Pn=p1pn were generated randomly using the computer algorithm described in Kvålseth (2015). Thus, the richness n2,100 and the value of each pi were generated as random numbers within given intervals. The results are summarized in Table 1.

TABLE 1.

Sample values from randomly generated distributions Pn=p1pn of the measures DS and DS* defined in (4), DS2 and DS2* in (6), H and H* in (5), and H2 and H2* in (7).

Data set n
DS
DS*
DS2
DS2*
H
H*
H2
H2*
1 5 0.62 0.78 2.62 0.41 1.20 0.75 3.32 0.58
2 30 0.50 0.52 2.00 0.03 1.31 0.39 3.71 0.09
3 62 0.92 0.94 12.63 0.19 3.55 0.86 34.81 0.55
4 70 0.24 0.24 1.31 0.00 0.85 0.20 2.34 0.02
5 78 0.88 0.89 8.02 0.09 3.48 0.80 32.46 0.41
6 78 0.81 0.82 5.33 0.06 3.08 0.71 21.76 0.27
7 88 0.97 0.98 38.77 0.43 4.20 0.94 66.69 0.76
8 10 0.73 0.81 3.71 0.30 1.72 0.75 5.58 0.51
9 39 0.87 0.89 7.56 0.17 2.91 0.79 18.36 0.46
10 26 0.96 1.00 24.50 0.94 3.23 0.99 25.28 0.97
11 79 0.90 0.91 10.20 0.12 3.24 0.74 25.53 0.31
12 36 0.11 0.11 1.13 0.00 0.42 0.12 1.52 0.01
13 90 0.91 0.92 11.21 0.11 3.51 0.78 33.45 0.36
14 19 0.84 0.89 6.43 0.30 2.48 0.84 11.94 0.61
15 75 0.90 0.91 9.82 0.12 3.49 0.81 32.79 0.43
16 43 0.93 0.95 14.84 0.33 3.41 0.91 30.27 0.70
17 71 0.91 0.92 10.79 0.14 3.44 0.81 31.19 0.43
18 19 0.90 0.95 9.55 0.48 2.68 0.91 14.59 0.76
19 42 0.62 0.64 2.66 0.04 2.09 0.56 8.08 0.17
20 17 0.67 0.71 3.02 0.13 1.86 0.66 6.42 0.34
21 11 0.01 0.01 1.01 0.00 0.02 0.01 1.02 0.00
22 95 0.96 0.97 22.85 0.23 4.16 0.91 64.07 0.67
23 91 0.02 0.02 1.02 0.00 0.09 0.02 1.09 0.00
24 68 0.96 0.97 22.32 0.32 3.90 0.92 49.40 0.72
25 82 0.75 0.76 4.02 0.04 2.81 0.64 16.61 0.19
26 12 0.86 0.94 6.96 0.54 2.26 0.91 9.58 0.78
27 20 0.88 0.93 8.31 0.38 2.61 0.87 13.60 0.66
28 17 0.38 0.40 1.60 0.04 1.08 0.38 2.94 0.12
29 21 0.74 0.78 3.83 0.14 1.94 0.64 6.96 0.30
30 91 0.30 0.30 1.42 0.00 1.16 0.26 3.19 0.02

While some of the measures included in Table 1 will be defined in subsequent derivations, one conclusion that can be drawn from the data for the diversity measures in (4)–(7) is that no apparent relationship seems to exist between richness and evenness. Based on the statistical results for the Pearson correlation coefficient (r) for Data Sets 1–4 in Table 2, the absolute values of the t‐statistic are all less than the critical value t28,α/2=2.048 for the significance level α=0.05 so that the null‐hypothesis of zero (population) correlation cannot be rejected. Similarly, from the four p‐values in Table 2, there is sufficient evidence to conclude that the correlation between richness and evenness for each of the diversity measures in (4)–(7) is not significantly different from zero. Of course, zero correlation does not necessarily imply statistical independence since other than linear relationships may exist between evenness and richness. However, from the data in Table 1, no other potential relationship seems plausible.

TABLE 2.

Pearson's correlation coefficients (r) and the t‐statistics for the null hypothesis that the population correlation ρ=0 (versus ρ0) as well as the p‐values based on the data in Table 1.

Data set r r‐value t‐statistic p‐value
1
rDS*n
.04 0.21 .84
2
rDS2*n
−.35 −1.97 .06
3
rH*n
−.01 −0.05 .96
4
rH2*n
−.18 −0.97 .34
5
rDS*DS2*
.60 3.97 .0005
6
rH*H2*
.90 10.93 .00001
7
rDS*H*
.99 37.14 .00001
8
rDS2*H2*
.89 10.33 .00001
9
rDSH
.93 13.39 .00001
10
rDSDS2
.64 4.41 .000 1
11
rHH2
.88 9.80 .00001
12
rDS2H2
.89 10.33 .00001

It is important to point out that even though the values of the different evenness indices are found to be highly correlated as shown in Table 2 (Data Sets 5–8), their individual values can differ greatly as seen from the results in Table 1. For example, when comparing DS* and DS2*, RMSEDS*DS2*=i=130DSi*DS2i*2/301/2=0.58 and RMSEH*H2*=0.28. Similarly differing results are seen when comparing the diversity values in Table 1. Although the correlation coefficients in Table 2 (Data Sets 9–12) are quite impressive, different diversity measures can produce substantially different results for the same distributions Pn=p1pn. For example, for DS2 in (6) and H2 in (7), which both take on values within the same [1, n]‐interval, it is found that RMSEDS2H2=15.18. Comparative results such as these give reason for concern when using even some of the most popular measures of diversity and evenness. However, such concern is alleviated in the subsequent richness‐evenness analysis, where value‐validity corrections are being applied to the evenness indices.

4. RICHNESS‐EVENNESS TRADEOFF

4.1. General tradeoff formulation

While the preceding analysis is concerned with potential relationships between richness and evenness, or lack thereof, when based on varying distributions Pn=p1pn, consider now the following question: what are the relative effects of richness and evenness on a given diversity measure for any individual distribution Pn? That is, what is the tradeoff between richness and evenness for any given diversity value DPn? Or, how can different combinations of richness and evenness produce the same given DPn‐value?

The most obvious answer to this question would seem to lie in the definition in (3). Thus, for any given DPn, one could simply replace the Pn on the right side of (3) with any other distribution Pm=p1pm such that DPm=DPn and then solve the resulting equation for D*Pm as a function of m. However, since the evenness indices in (4)–(7) do not meet the value‐validity condition in (12) (Kvålseth, 2015), an alternative approach should be considered.

In terms of the lambda distribution Pnλ in (8) and a generic diversity measure D, the relationship in (10) can be generalized such that for any given Pn, the given value DPn can equal DPmλ for various unique mλ‐pairs. There would necessarily be a certain restriction on m depending upon the value DPn. For a chosen m, the DPmλ becomes a function of λ that can be solved for λ as the proper evenness value. The resulting λ may conveniently be denoted by DC*Pm, or simply DC*, to indicate that the normalized D* has been corrected to satisfy the value‐validity condition in (12).

This procedure may be summarized as follows: for any given DPn,

DPn=DPmλλ=DC*=fDPnm (14)

where f is a function of DPn and m. The formulation in (14) holds for any λ0,1 and all m subject to a restriction mm0DPn that depends on the value DPn and consequently on the form of the diversity measure as will be exemplified next for the diversity measures in (4)–(7). By varying m and DC* in (14), the results can also be represented graphically as richness‐evenness curves, or R‐E curves, for potentially interesting and useful diversity analysis.

4.2. Simpson's measures

For Simpson's index in (4), it follows from (14) and Pmλ defined in (9) that

DSPn=DSPmλ=11/mλ2λ (15)

which, solved for λ as the value‐validity corrected evenness DSC*, gives

λ=DSC*=11mDSPnm1 (16)

This relationship holds for all DSC*0,1 and m1/1DSPn (for the square root to be defined).

As a simple example, consider the distribution P5=0.40,0.30,0.15,0.10,0.05 for which DSP5=0.72 so that from (16),

DSC*=11m0.72m1

as the tradeoff relationship between the richness m and evenness DSC* for the fixed diversity value DSP5=0.72. The resulting graph of DSC* as a function of m for m1/10.72=3.57 (or 4) becomes the R‐E (tradeoff) curve for DSP5=0.72. By choosing, for instance, the richness value m=10, the corresponding evenness value (point) along the R‐E curve would be DSC*=11100.72/9=0.55.

Other diversity measures that are strictly increasing functions of DSPn will necessarily have the same richness‐evenness curve as that of DSPn for the same Pn. Such diversity measures include DS2Pn in (6), the statistical odds measure DS2Pn1 by Kvålseth (1991), logi=1npi2 proposed by Pielou (1977), 1i=1npi2/11/N by McIntosh (1967) where N is the sample size, and 1i=1npi2 proposed by Junge (1994). As an example of this fact, consider the form DS2Pn of Simpson's index in (6) for which

DS2Pn=DS2Pmλ=111mλ2λ1

with Pmλ defined in (8). Solving this expression for λ as the value‐validity corrected evenness λ=DS2C*, it is readily seen that DS2C* as a function of DS2Pn and m is exactly the same as that of (16) with DSPn=1DS2Pn1.

Examples of such curves are given in Figure 1 based on real data from Magurran (2004), with DSP9=0.38 (p. 243, “Unburned forest”), DSP14=0.69 (p. 243, “Burned chaparral”), and DSP20=0.88 (pp. 237–238, “Derrycunnitry oakwood”). Those species abundance distributions cover a wide range of diversity values. These curves cover richness‐values for m30, although the asymptotic values of DSC*Pm are seen from (16) to be 11DSPn as m. The curves are presented as being continuous, but they are obviously most meaningful for integer values of m.

FIGURE 1.

FIGURE 1

Richness‐evenness curves for Simpson's index from (16) for three different abundance distributions (see text).

4.3. Entropy measures

In order to obtain the R‐E curve for the commonly used entropy HPn in (5), it becomes immediately clear that setting HPn=HPmλ for any given abundance distribution Pn and the lambda distribution Pmλ in (8) cannot be readily solved for λ=HC* as required by (14). One could, of course, use a search procedure to obtain all combinations for m and λ such that HPn=HPmλ for any given HPn. Alternatively, as a more convenient and practical approach, good approximate results can be obtained from the following formulation by Kvålseth (2014):

λHC*=11HPnlogm4/3α,α=12m11/9 (17)

All combinations of m and HC* in (17) have the same entropy value HPn, with mexpHPn and HC* being the (approximate) value‐validity corrected evenness index for HPn.

As a computational example, consider P5=0.40,0.30,0.15,0.10,0.05 as used above for DSC*. With HP5=1.39 and for m=n=5, it follows from (17) that α=0.58 and hence HC*P5=0.63. By choosing, say, m=10, it is found from (17) that α=0.64 and hence HC*P10=0.37. The comparable values for DSC* from (16) are DSC*Pm=0.68and0.55, indicating that individual values of DSC* and HC* can differ considerably. As with alternative diversity measures that are strictly increasing functions of DSPn, those that are strictly increasing functions of HPn such as H2Pn in (7) will have the same R‐E curve as that of HPn for any given Pn.

As examples of R‐E curves for HPn involving real biological data, those used for DSPn and represented by Figure 1 will also be used for HPn with the respective values HP9=0.88, HP14=1.65, and HP20=2.41. The three curves are given in Figure 2.

FIGURE 2.

FIGURE 2

Richness‐evenness curves for the entropy index from (17) for the same three different abundance distributions as those used in Figure 1 (see text).

4.4. Comments on the R‐E curves

The general richness‐evenness (R‐E) curve is based on evenness DC*Pm, or simply DC*, as a function of the richness m for some given (fixed) entropy value DPn as expressed in (14). Some general properties of an R‐E curve are as follows. First, each point (m, DC*) on the curve has the same entropy value DPn. In order to produce such a curve, which is somewhat analogous in shape to the indifference curve used in economics (e.g., Varian, 2010), only the diversity value DPn and the form of D need to be known. Second, the R‐E curve is convex (i.e., bowed toward the origin). Third, the R‐E curve has a negative slope. Fourth, since the function f in (14) is assumed to be a single‐valued function, R‐E curves cannot intersect. Fifth, curves with increasing distance from the origin represent increasing diversity.

These properties are all rather evident from the real data curves in Figures 1 and 2. Although the general shapes of the curves are quite similar for Simpson's DS in (4) and the entropy H in (5), their specific details clearly differ considerably. Even though one of the properties of R‐E curves is that they cannot intersect for the same diversity measure, they can for different diversity measures as is apparent from Figures 1 and 2. Thus, for instance, the middle curves for DSP14=0.69 and HP14=1.65 are seen to intercept approximately at the point when m=8 and DSC*P8=HC*P8=0.55. At this crossover point, the DSP14 and HP14 have the same richness and evenness components, otherwise they differ for this P14‐distribution. For m>8, the rate of change of evenness with increasing m is clearly greater for HP14 than for DSP14, whereas for m<8, this rate of change is more comparable.

One of the most striking characteristics common to all of these R‐E curves is the rather dramatic negative slopes for the smaller m values where the evenness values approach unity as m approaches the respective lower limits of 1/1DSPn and expHPn. That is, for a given or constant diversity value DPn and for any other distribution Pm=p1pm such that DPm=DPn, the evenness is most sensitive to changes in m for small m‐values.

The fact that the actual richness m=n and evenness DC*Pn is a single point on an R‐E curve representing a given diversity value DPn, such as the points identified in Figures 1 and 2, indicates the considerable amount of potentially interesting and useful information available in such a curve. The use of such information depends, of course, on the particular interest of a user or researcher in any given situation. With all points along an R‐E curve having the same diversity, perhaps the single most useful aspect lies in the ability to see how the diversity components, richness and evenness, can be traded off and still produce the same diversity as that of the original data set. Far from being independent, richness depends entirely on evenness, or vice versa, for any given R‐E curve.

While an individual R‐E curve can provide information about the potential richness‐evenness tradeoff characteristic for a particular data set or diversity value, different R‐E curves can also be used for comparing the diversity values for different data sets or distributions Pn when controlling for either richness or evenness. As an example, consider the three curves in Figure 1 and control for m by looking at the point on each curve with say, m=20. For the top curve, this point corresponds to the diversity DSP20=0.88 for the real P20 from Magurran (2004, pp. 237–238). Comparing the DSC* values for the three points with m=20 shows how the differences between the three diversity values (0.38, 0.69, and 0.88) are due to the equal differences between the respective evenness values of 0.23, 0.48, and 0.73 as seen from Figure 1 or computed from (16).

As stated at the beginning of Section 4, the tradeoff between richness and evenness for any given diversity value DPn could also be considered in terms of (3) as

DPm=DPm1DPm0D*Pm+DPm0=DPn

and then simply determine D*Pm as a function of m. The resulting richness‐evenness curves would at least resemble in form those of DC* versus m as presented above and would be entirely appropriate if D*Pm is assumed to be an acceptable evenness measure. However, since this assumption can indeed be challenged for various diversity measures (Kvålseth, 2015), the value‐validity corrected evenness measures DC*Pm are used as a more appropriate representation. Also, while the value‐validity requirement is discussed quite concisely in this article, more detailed explanations are given by Kvålseth (2011, 2014, 2015).

4.5. Relative effects of richness and evenness

It is rather evident from the data in Table 1 that evenness generally contributes more toward diversity than does richness or that diversity is more sensitive to changes in evenness than to changes in richness. Since the range of variation of those two characteristics differs greatly, one reasonable way to compare their effects on diversity is to consider relative changes in diversity related to relative changes in evenness and richness by a method analogous to partial elasticity widely used in economics (e.g., Varian, 2010, pp. 274–291).

Thus, in terms of relative changes and partial derivatives, one can define the following measure for DS in (4):

EDS*=limDS*0DS/DSDS*/DS*=DSDS*DS*DS (18)

which measures the sensitivity of DS to a (relative) change in DS* while keeping richness n fixed. Also, by treating n as a continuous variable for purely mathematical purpose and by similarly defining En as in (18), the following result is obtained:

EDS*=nn1En (19)

That is, for n>2, DS is more sensitive to changes in evenness than to changes in richness (n), especially for large n.

Similarly, for the entropy measure in (5) and the equivalent relative change expressions for H* and n to that of (18), it is determined that

EH*=lognEn (20)

which shows that, for n>2, the entropy index is more sensitive to changes in H* than to changes in n. When comparing (19) and (20), it would seem that such differences between evenness and richness in their effects on diversity are more pronounced in the case of DS in (4) than of H in (5).

In terms of the same definition as in (18), the following result is obtained for DS2 in (6) and H2 in (7):

EDS2*=11nEn,EH2*=11nEn (21)

The inference from (21) is that both diversity measures DS2 and H2 tend to be somewhat less sensitive to changes in evenness than to changes in richness, but only marginally so when n is large. Interestingly, this finding is opposite those in (19) and (20).

5. CONCLUSION

There are three main findings from this analysis. First, when considering the results from randomly generated abundance distributions Pn=p1pn for the four well‐known diversity measures in (4)–(7), the conclusion is that there is no statistically significant correlation between the richness and evenness components of those diversity measures. Second, in spite of such lack of association between richness and evenness across abundance distributions, one can analyze the relationship between richness and evenness for any given Pn and any diversity index by means of the richness‐evenness curve introduced above. Third, when considering relative changes in the values of a diversity measure as the result of a relative change in richness (with evenness kept fixed) versus a relative change in evenness (with richness kept fixed), DS in (4)and H in (5) are found to be more sensitive to changes in evenness than to richness, with the reverse finding for DS2 in (6) and H2 in (7).

The richness‐evenness (R‐E) curve provides a new tool for analyzing diversity. Such a curve can provide interesting and useful information about the potential tradeoff between the richness and evenness components of a given value of any diversity measure. It also has potential utility when comparing the diversity values for different abundance distributions and when comparing the behavior of different diversity measures.

AUTHOR CONTRIBUTIONS

Tarald O. Kvålseth: Conceptualization (equal); data curation (equal); formal analysis (equal); funding acquisition (equal); investigation (equal); methodology (equal); project administration (equal); resources (equal); software (equal); supervision (equal); validation (equal); visualization (equal); writing – original draft (equal); writing – review and editing (equal).

FUNDING INFORMATION

None.

CONFLICT OF INTEREST STATEMENT

The author declares no conflict of interest.

ACKNOWLEDGMENTS

None.

Kvålseth, T. O. (2024). Diversity analysis: Richness versus evenness. Ecology and Evolution, 14, e70275. 10.1002/ece3.70275

DATA AVAILABILITY STATEMENT

All relevant data are included in the manuscript.

REFERENCES

  1. Blowes, S. A. , Daskalova, G. N. , Dornelas, M. , Engel, T. , Gotelli, N. J. , Magurran, A. E. , Martins, I. S. , Mcgill, B. , McGlinn, D. J. , Sagouis, A. , Shimadzu, H. , Supp, S. R. , & Chase, J. M. (2022). Local biodiversity change reflects interactions among changing abundance, evenness, and richness. Ecology, 103(12), e3820. 10.1002/ecy.3820 [DOI] [PubMed] [Google Scholar]
  2. Bock, C. E. , Jones, Z. F. , & Bock, J. H. (2007). Relationships between species richness, evenness, and abundance in a southwestern savanna. Ecology, 88(5), 1322–1327. [DOI] [PubMed] [Google Scholar]
  3. Buzas, M. A. , & Hayek, L. A. C. (2005). On richness and evenness within and between communities. Paleobiology, 31(2), 199–220. [Google Scholar]
  4. Daly, A. J. , Baetens, J. M. , & De Baets, B. (2018). Ecological diversity: Measuring the unmeasurable. Mathematics, 6, 119. 10.3390/math6070119 [DOI] [Google Scholar]
  5. Gosselin, F. (2006). An assessment of the dependence of evenness indices on species richness. Journal of Theoretical Biology, 242(3), 591–597. [DOI] [PubMed] [Google Scholar]
  6. Heip, C. (1974). A new index measuring evenness. Journal of the Marine Biological Association of the United Kingdom, 54(3), 555–557. [Google Scholar]
  7. Jost, L. (2010). The relation between evenness and diversity. Diversity, 2(2), 207–232. [Google Scholar]
  8. Junge, K. (1994). Diversity of ideas about diversity measurement. Scandinavian Journal of Psychology, 35(1), 16–26. [Google Scholar]
  9. Kvålseth, T. O. (1991). Note on biological diversity, evenness, and homogeneity measures. Oikos, 62, 123–127. [Google Scholar]
  10. Kvålseth, T. O. (2011). The lambda distribution and its applications to categorical summary measures. Advances and Applications in Statistics, 24(2), 83–106. [Google Scholar]
  11. Kvålseth, T. O. (2014). Entropy evaluation based on value validity. Entropy, 16(9), 4855–4873. [Google Scholar]
  12. Kvålseth, T. O. (2015). Evenness indices once again: Critical analysis of properties. Springerplus, 4(232), 1–12. [DOI] [PMC free article] [PubMed] [Google Scholar]
  13. Liu, C. , Sun, T. , Wu, X. , tan, L. , Cai, Q. , & Tang, T. (2023). Disentangling multiple relationships of species diversity, functional diversity, diatom community biomass and environmental variables in a mountainous watershed. Frontiers in Ecology and Evolution, 11, 1150001. 10.3389/fevo.2023.1150001 [DOI] [Google Scholar]
  14. Ma, M. (2005). Species richness vs evenness: Independent relationship and different responses to edaphic factors. Oikos, 111(1), 192–198. [Google Scholar]
  15. Magurran, A. E. (2004). Measuring biological diversity. Blackwell Science. [Google Scholar]
  16. McIntosh, R. P. (1967). An index of diversity and the relation of certain concepts to diversity. Ecology, 48(3), 392–404. [Google Scholar]
  17. Peet, R. K. (1974). The measurement of species diversity. Annual Review of Ecology and Systematics, 5(1), 285–307. [Google Scholar]
  18. Pielou, E. C. (1977). Mathematical ecology. Wiley. [Google Scholar]
  19. Shannon, C. E. (1948). A mathematical theory of communication. The Bell System Technical Journal, 27(3), 379–423, 623‐656. [Google Scholar]
  20. Sheldon, A. L. (1969). Equitability indices: Dependence on the species count. Ecology, 50(3), 466–467. [Google Scholar]
  21. Simpson, E. H. (1949). Measurement of diversity. Nature, 163, 688. 10.1038/163688a0 [DOI] [Google Scholar]
  22. Smith, B. , & Wilson, J. B. (1996). A consumer's guide to evenness indices. Oikos, 76, 70–82. [Google Scholar]
  23. Soininen, J. , Passy, S. , & Hillebrand, H. (2012). The relationship between species richness and evenness: A meta‐analysis of studies across aquatic ecosystems. Oecologia, 169, 803–809. [DOI] [PubMed] [Google Scholar]
  24. Stirling, G. , & Wilsey, B. (2001). Empirical relationships between species richness, evenness, and proportional diversity. The American Naturalist, 158(3), 286–299. [DOI] [PubMed] [Google Scholar]
  25. Su, Q. (2018). A relationship between species richness and evenness that depends on specific relative abundance distribution. PeerJ, 6, e4951. 10.7717/peerj.4951 [DOI] [PMC free article] [PubMed] [Google Scholar]
  26. Varian, H. R. (2010). Intermediate microeconomics (8th ed.). W. W. Norton. [Google Scholar]
  27. Yan, H. , Li, F. , & Liu, G. (2023). Diminishing influence of negative relationship between species richness and evenness on the modeling of grassland α‐diversity metrics. Frontiers in Ecology and Evolution, 11, 1108739. 10.3389/fevo.2023.1108739 [DOI] [Google Scholar]
  28. Zhang, H. , John, R. , Peng, Z. , Yuan, J. , Chu, C. , Du, G. , & Zhou, S. (2012). The relationship between species richness and evenness in plant communities along a successional gradient: A study from sub‐alpine meadows of the eastern Qinghai‐Tibetan plateau, China. PloS One, 7(11), e49024. 10.1371/journal.pone.0049024 [DOI] [PMC free article] [PubMed] [Google Scholar]

Associated Data

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Data Availability Statement

All relevant data are included in the manuscript.


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