# Chapter 9 Types of distance coefficients

There are three groups of distance coefficients: *metrics*, *semimetrics*, and *nonmetrics* .

## 9.1 Metric distances

The first group consists of *metrics*, and its coefficients satisfy the following properties:

minimum 0: if species \(a\) is equal to species \(b\), then \(D(a,b)=0\); ✅

positiveness: if \(a \neq b\), then \(D(a,b) > 0\); ✅

symmetry: \(D(a,b) = D(b,a)\); ✅

triangle inequality: \(D(a,b) + D(b,c) \geq D(a,c)\). The sum of two sides of a triangle drawn in the Euclidean space is equal or greater than the third side. ✅

We can spot all these properties below:

`as.matrix(dist(spe))[1:6, 1:6]`

```
## 1 2 3 4 5 6
## 1 0.000000 5.385165 7.416198 7.874008 10.816654 7.348469
## 2 5.385165 0.000000 2.449490 4.123106 10.677078 4.582576
## 3 7.416198 2.449490 0.000000 3.000000 10.862780 4.123106
## 4 7.874008 4.123106 3.000000 0.000000 9.219544 2.828427
## 5 10.816654 10.677078 10.862780 9.219544 0.000000 8.185353
## 6 7.348469 4.582576 4.123106 2.828427 8.185353 0.000000
```

### 9.1.1 Euclidean distances

The most common metric distance measure is the *Euclidean distance*.

Euclidean distance is a measure of the distance between two points in Euclidean space. In two dimensions, the Euclidean distance between two points (x1, y1) and (x2, y2) can be calculated using the Pythagorean theorem:

\[D_{1} (x_1,x_2) = \sqrt{\sum_{j=1}^p(y_{1j} - y_{2j})^2}\]

Euclidean distance is a commonly used measure in multivariate analyses because it provides a straightforward and intuitive way to measure the distance or similarity between observations in a multidimensional space.

Using `stats::dist()`

, we can compute it with:

`<- dist(x = spe, method = "euclidean") spe.D.Euclid `

And, we can test whether a distance is Euclidean using:

`is.euclid(spe.D.Euclid)`

`## [1] TRUE`

### 9.1.2 Challenge #1

**Your turn!** Using the `dist()`

function, compute the Euclidean distance matrix \(D_{hmm}\) for the species abundances by site matrix \(Y_{hmm}\) below:

Sites | \(y_1\) | \(y_2\) | \(y_3\) |
---|---|---|---|

\(s_1\) | 0 | 4 | 8 |

\(s_2\) | 0 | 1 | 1 |

\(s_3\) | 1 | 0 | 0 |

```
<- data.frame(y1 = c(0, 0, 1), y2 = c(4, 1, 0), y3 = c(8,
Y.hmm 1, 0))
```

After this, look into the numbers, think critically about them!

**Solution:**

You should have something similar to this:

```
<- dist(x = Y.hmm, method = "euclidean")
Y.hmm.DistEu
as.matrix(Y.hmm.DistEu)
```

```
## 1 2 3
## 1 0.000000 7.615773 9.000000
## 2 7.615773 0.000000 1.732051
## 3 9.000000 1.732051 0.000000
```

*Now, look into the composition and the distances between sites* \(s_2\) and \(s_3\) and between \(s_1\) and \(s_2\). What is going on?

The Euclidean distance between sites \(s_2\) and \(s_3\), which have no species in common, is smaller than the distance between \(s_1\) and \(s_2\), which share species \(y_2\) and \(y_3\) (!).

From an ecological perspective, *this is a problematic* assessment of the relationship among sites.

This issue is known as the **double-zero problem**, *i.e.* double zeroes are treated in the same way as double presences, so that the double zeros shrink the distance between two sites.

Euclidean distances ( \(D_1\) ) should thus *not* be used to compare sites based on species abundances.

### 9.1.3 Chord distances

Orlóci (1967) proposed the *Chord distance* to analyse community composition.

Chord distance, also known as angular distance or great-circle distance, is a measure of the distance between two points on a sphere, such as the Earth.

It consists of:

1. Normalizing the data, *i.e.* scaling site vectors to length 1 by dividing species abundances in a given sample by the square-rooted sum of square abundances in all samples as

\[y'_{Uj}=y_{Uj}/\sum^s_{j=1}{y^2_{Uj}}\]

2. Calculating the Euclidean distances on this normalized data:

\[D_{3} (x_1,x_2) = \sqrt{\sum_{j=1}^p(y'_{1j} - y'_{2j})^2}\]

We can use `vegan::vegdist()`

for this one:

`<- vegdist(spe, method = "chord") spe.D.Ch `

```
## Warning in vegdist(spe, method = "chord"): you have empty rows: their dissimilarities may be
## meaningless in method "chord"
```

`## Warning in vegdist(spe, method = "chord"): missing values in results`

`as.matrix(spe.D.Ch)[1:3, 1:3]`

```
## 1 2 3
## 1 0.0000000 0.7653669 0.9235374
## 2 0.7653669 0.0000000 0.2309609
## 3 0.9235374 0.2309609 0.0000000
```

When two sites share the same species in the same proportions of the number of individuals the value of \(D_3\) is \(0\), and when no species are shared, its value is \(\sqrt{2}\).

*What happens if we compute Chord distances in the same site-by-species matrix* \(Y_{hmm}\)?

Let us try the Chord distances in the same matrix we used for Challenge #1:

`<- vegdist(Y.hmm, method = "chord") Y.hmm.DistCh `

`as.matrix(Y.hmm.DistCh)`

```
## 1 2 3
## 1 0.0000000 0.3203645 1.414214
## 2 0.3203645 0.0000000 1.414214
## 3 1.4142136 1.4142136 0.000000
```

Now, let us compare with what we obtained when we used Euclidean distances:

`as.matrix(Y.hmm.DistEu)`

```
## 1 2 3
## 1 0.000000 7.615773 9.000000
## 2 7.615773 0.000000 1.732051
## 3 9.000000 1.732051 0.000000
```

See again how our matrix looks:

` Y.hmm`

```
## y1 y2 y3
## 1 0 4 8
## 2 0 1 1
## 3 1 0 0
```

So, adding any number of double zeroes to a pair of sites does *not* change the value of \(D_3\). Hence, *Chord distances* can be used to compare sites described by species abundances!

### 9.1.4 Jaccard’s coefficient

Another popular association coefficient is the *Jaccard similarity coefficient* (1900).

The Jaccard similarity coefficient was originally proposed by the French mathematician Paul Jaccard in 1901, in the context of ecology. Jaccard was interested in comparing the species composition of different plant communities, and proposed the Jaccard index as a measure of similarity between two communities based on their species richness.

Jaccard’s similarity coefficient is only appropriate for **binary data**, and its distance coefficient is defined with the size of the intersection divided by the size of the union of the sample sets.

\[D_{7}(x_1,x_2) = 1 - \frac{\vert x_1 \cap x_2 \vert}{\vert x_1 \cup x_2 \vert} = 1 - \frac{\vert x_1 \cap x_2 \vert}{\vert x_1 \vert + \vert x_2 \vert - \vert x_1 \cap x_2 \vert} = 1-\frac{a}{a+b+c}\]

where,

- \(a\) is the number of species shared between \(x_1\) and \(x_2\) that are coded \(1\);
- \(b\) is the number of occurrences where \(x_1\) and \(x_2\) are known to be different;
- \(c\) is the number of common absences between \(x_1\) and \(x_2\),
*i.e.*both \(0\).

For example, for sites \(x_1\) and \(x_2\):

\(x_1,x_2\) | \(y_1\) | \(y_2\) | \(y_3\) | \(y_4\) | \(y_5\) |
---|---|---|---|---|---|

\(x_1\) | 0 | 1 | 0 | 1 | 0 |

\(x_2\) | 0 | 1 | 1 | 1 | 1 |

So, we can calculate \(a\), \(b\), and \(c\): - \(a\) = 1 + 1 = 2

\(b\) = 1 + 1 = 2

\(c\) = 1

And, then our distance coefficient:

\[D_{7}(x_1,x_2) = 1-\frac{2}{2+2+1}= 0.6\]

In `R`

, you can use use the `vegan::vegdist()`

function to calculate the Jaccard’s coefficient:

`<- vegdist(spe, method = "jaccard", binary = TRUE) spe.D.Jac `

```
## Warning in vegdist(spe, method = "jaccard", binary = TRUE): you have empty rows: their dissimilarities may be
## meaningless in method "jaccard"
```

## 9.2 Semimetric distances

The second group consists of *semimetrics*, and they violate the *triangle inequality* property:

minimum 0: if species \(a\) is equal to species \(b\), then \(D(a,b)=0\); ✅

positiveness: if \(a \neq b\), then \(D(a,b) > 0\); ✅

symmetry: \(D(a,b) = D(b,a)\); ✅

~~triangle inequality~~: \({D(a,b) + D(b,c) \geq or < D(a,c)}\). The sum of two sides of a triangle drawn in the Euclidean space is*not*equal or greater than the third side. ❌

### 9.2.1 Sørensen’s coefficient

All parameters in *Jaccard’s similarity coefficient* have equal weights.

\[D_{7}(x_1,x_2)=1-\frac{a}{a+b+c}\]

However, you may want to consider that a presence of a species is more informative than its absence.

The distance corresponding to *Sørensen’s similarity coefficient* (1948) gives weight to double presences:

\[D_{13}(x_1,x_2)=1-\frac{2a}{2a+b+c}=\frac{b+c}{2a+b+c}\]

where,

- \(a\) is the number of species shared between \(x_1\) and \(x_2\) that are coded \(1\);
- \(b\) is the number of occurrences where \(x_1\) and \(x_2\) are known to be different;
- \(c\) is the number of common absences between \(x_1\) and \(x_2\),
*i.e.*both \(0\).

In `R`

, you can also use the `vegan::vegdist()`

function to calculate the Sørensen’s coefficient:

`<- vegdist(spe, method = "bray", binary = TRUE) spe.D.Sor `

```
## Warning in vegdist(spe, method = "bray", binary = TRUE): you have empty rows: their dissimilarities may be
## meaningless in method "bray"
```

Because both Jaccard’s and Sørensen’s are only appropriate for presence-absence data, you must binary-transform abundance data using

`binary = TRUE`

in`vegdist()`

.

### 9.2.2 Bray-Curtis’ coefficient

The *Bray-Curtis dissimilarity coefficient* is a modified version of the Sørensen’s index and allows for species abundances:

\[D_{14}(x_1,x_2)=\frac{\sum{\vert y_{1j}-y_{2j}\vert}}{\sum{( y_{1j}+y_{2j})}}=\]

\[D_{14}(x_1,x_2)=1 - \frac{2W}{A+B}\]

where,

\(W\) is the sum of the lowest abundances in each species found between sites \(x_1\) and \(x_2\);

\(A\) is the sum of all abundances in \(x_1\); and,

\(B\) is the sum of all abundances in \(x_2\).

For example, for sites \(x_1\) and \(x_2\):

\(x_1,x_2\) | \(y_1\) | \(y_2\) | \(y_3\) | \(y_4\) | \(y_5\) |
---|---|---|---|---|---|

\(x_1\) | 2 |
1 |
0 |
5 | 2 |

\(x_2\) | 5 | 1 |
3 | 1 |
1 |

So:

\(W = 2 + 1 + 0 + 1 + 1 = 5\)

\(A = 2 + 1 + 0 + 5 + 0 = 8\)

\(B = 5 + 1 + 3 + 1 + 2 = 12\)

\[D_{14}(x_1,x_2) = 1-\frac{2 \times 5}{8+12} = 0.5\]

To calculate the *Bray-Curtis dissimilarity coefficient*, which can account for abundances, you need to set `binary = FALSE`

.

`<- vegdist(spe, method = "bray", binary = FALSE) spe.db.pa `

```
## Warning in vegdist(spe, method = "bray", binary = FALSE): you have empty rows: their dissimilarities may be
## meaningless in method "bray"
```

`<- as.matrix(spe.db.pa) spe.db `

## 9.3 Nonmetric distances

Non-metric distances do not satisfy the metric properties of symmetry, triangle inequality, and identity of indiscernibles:

minimum 0: if species \(a\) is equal to species \(b\), then \(D(a,b)=0\); ✅

~~positiveness:~~if \(a \neq b\), then \(D(a,b) > or < 0\); ❌symmetry: \(D(a,b) = D(b,a)\); ✅

~~triangle inequality~~: \({D(a,b) + D(b,c) \geq or < D(a,c)}\). The sum of two sides of a triangle drawn in the Euclidean space is*not*equal or greater than the third side. ❌

### 9.3.1 Mahalanobis distance

The Mahalanobis distance between a point \(x\) and a group of points with mean \(\mu\) and covariance \(\Sigma\) is defined as:

\[ D_{M}(x, \mu)=\sqrt{(x-\mu)^{T} \Sigma^{-1}(x-\mu)} \]

where \(T\) denotes the transpose, and \(\Sigma^{-1}\) is the inverse (or generalized inverse) of the covariance matrix \(\Sigma\).

The Mahalanobis distance is a measure of the distance between a point and a group of points, taking into account the covariance structure of the data.

The inverse of the covariance matrix may not exist in some cases, such as when the variables are linearly dependent or when there are more variables than observations. In these cases, we can use the generalized inverse of the covariance matrix instead of the inverse to calculate the Mahalanobis distance.

This generalized inverse can be calculated using various methods, such as the Moore-Penrose pseudoinverse or the singular value decomposition.

```
# Create a matrix
<- matrix(rnorm(100 * 3), ncol = 3)
x
# Compute the covariance matrix and its generalized inverse
<- cov(x)
cov_mat <- MASS::ginv(cov_mat)
cov_inv
# Compute the Mahalanobis distance using the generalized
# inverse
<- mahalanobis(x, colMeans(x), cov_inv)
mah_dist
# Print the Mahalanobis distance
mah_dist
```

```
## [1] 5.3061344 0.4564071 0.5675535 2.6662348 2.6104018 2.8003909
## [7] 0.7387431 1.6389466 2.0946018 2.4312276 4.1154981 0.6594897
## [13] 1.5999119 1.6972242 1.3342990 1.9901599 1.7357188 3.3316827
## [19] 0.5151656 3.9368640 5.2791708 5.1663413 2.8405269 0.7353339
## [25] 1.9673492 0.3209718 6.9408993 3.3828410 5.1428101 0.5353325
## [31] 8.5139202 3.0309815 0.7104318 0.9032237 2.3282240 3.0346249
## [37] 5.4598914 0.1983710 4.1290330 4.2982019 2.5967636 0.9382021
## [43] 0.8371468 4.0157851 1.8016870 4.9426385 4.7946697 0.2282839
## [49] 2.0152140 2.5913860 0.5940376 2.6276484 4.2863809 1.4615368
## [55] 3.1716714 7.5784045 4.5591584 0.9571423 1.6410469 4.5505595
## [61] 1.3234568 3.8684175 1.6439035 2.8403670 2.3683293 2.4394518
## [67] 0.1457964 0.5843688 2.2891974 2.2350074 2.3389038 1.7066545
## [73] 11.6688333 0.4188703 5.8838899 2.7220653 0.9200645 1.9423320
## [79] 1.8693955 0.8986885 0.1474006 1.0547710 1.0659005 5.6092933
## [85] 3.0226432 3.1002519 3.8087669 1.3096003 0.6523915 1.5947396
## [91] 10.6049817 0.9768489 7.7914822 1.5312161 1.4748627 1.4869509
## [97] 4.9946700 1.6155105 2.7046948 1.1386726
```

## 9.4 Representing distance matrices

We can create graphical depictions of association matrices using the `coldiss()`

function:

```
# coldiss() function Color plots of a dissimilarity matrix,
# without and with ordering License: GPL-2 Author: Francois
# Gillet, 23 August 2012
"coldiss" <- function(D, nc = 4, byrank = TRUE, diag = FALSE) {
require(gclus)
if (max(D) > 1)
<- D/max(D)
D
if (byrank) {
<- dmat.color(1 - D, cm.colors(nc))
spe.color else {
} <- dmat.color(1 - D, byrank = FALSE, cm.colors(nc))
spe.color
}
<- order.single(1 - D)
spe.o <- spe.color[spe.o, spe.o]
speo.color
<- par(mfrow = c(1, 2), pty = "s")
op
if (diag) {
plotcolors(spe.color, rlabels = attributes(D)$Labels,
main = "Dissimilarity Matrix", dlabels = attributes(D)$Labels)
plotcolors(speo.color, rlabels = attributes(D)$Labels[spe.o],
main = "Ordered Dissimilarity Matrix", dlabels = attributes(D)$Labels[spe.o])
else {
} plotcolors(spe.color, rlabels = attributes(D)$Labels,
main = "Dissimilarity Matrix")
plotcolors(speo.color, rlabels = attributes(D)$Labels[spe.o],
main = "Ordered Dissimilarity Matrix")
}
par(op)
}
# Usage: coldiss(D = dissimilarity.matrix, nc = 4, byrank =
# TRUE, diag = FALSE) If D is not a dissimilarity matrix
# (max(D) > 1), then D is divided by max(D) nc
# \t\t\t\t\t\t\tnumber of colours (classes) byrank=
# TRUE\t\tequal-sized classes byrank= FALSE\t\tequal-length
# intervals diag = TRUE\t\t\tprint object labels also on
# the diagonal
# Example: coldiss(spe.dj, nc=9, byrank=F, diag=T)
```

`coldiss(spe.D.Jac)`

You can also use `ggplot2::ggplot()`

to represent your matrix using `geom_tile()`

:

```
# obtain the order of the rows and columns
<- hclust(spe.D.Jac, method = "complete")$order
order_spe.D.Jac
# reorder the matrix to produce an figure ordered by
# similarities
<- as.matrix(spe.D.Jac)[order_spe.D.Jac,
order_spe.D.Jac_matrix
order_spe.D.Jac]
# converts to data frame
<- reshape2::melt(as.matrix(order_spe.D.Jac_matrix))
molten_spe.D.Jac
# create ggplot object
ggplot(data = molten_spe.D.Jac, aes(x = Var1, y = Var2, fill = value)) +
geom_tile() + scale_fill_gradient(low = "white", high = "black") +
theme_minimal()
```