designdist.RdFunction designdist lets you define your own dissimilarities
  using terms for shared and total quantities, number of rows and number
  of columns. The shared and total quantities can be binary, quadratic
  or minimum terms. In binary terms, the shared component is number of
  shared species, and totals are numbers of species on sites. The
  quadratic terms are cross-products and sums of squares, and minimum
  terms are sums of parallel minima and row totals. Function
  chaodist lets you define your own dissimilarities using terms
  that are supposed to take into account the “unseen species”
  (see Chao et al., 2005 and Details in vegdist).
designdist(x, method = "(A+B-2*J)/(A+B)", terms = c("binary", "quadratic", "minimum"), abcd = FALSE, alphagamma = FALSE, name) chaodist(x, method = "1 - 2*U*V/(U+V)", name)
| x | Input data. | 
|---|---|
| method | Equation for your dissimilarities. This can use terms
     | 
| terms | How shared and total components are found. For vectors
     | 
| abcd | Use 2x2 contingency table notation for binary data: \(a\) is the number of shared species, \(b\) and \(c\) are the numbers of species occurring only one of the sites but not in both, and \(d\) is the number of species that occur on neither of the sites. | 
| alphagamma | Use beta diversity notation with terms
     | 
| name | The name you want to use for your index. The default is to
    combine the  | 
Most popular dissimilarity measures in ecology can be expressed with
  the help of terms J, A and B, and some also involve
  matrix dimensions N and P. Some examples you can define in
  designdist are:
| A+B-2*J | "quadratic" | squared Euclidean | 
| A+B-2*J | "minimum" | Manhattan | 
| (A+B-2*J)/(A+B) | "minimum" | Bray-Curtis | 
| (A+B-2*J)/(A+B) | "binary" | Sørensen | 
| (A+B-2*J)/(A+B-J) | "binary" | Jaccard | 
| (A+B-2*J)/(A+B-J) | "minimum" | Ružička | 
| (A+B-2*J)/(A+B-J) | "quadratic" | (dis)similarity ratio | 
| 1-J/sqrt(A*B) | "binary" | Ochiai | 
| 1-J/sqrt(A*B) | "quadratic" | cosine complement | 
| 1-phyper(J-1, A, P-A, B) | "binary" | Raup-Crick (but see raupcrick) | 
The function designdist can implement most dissimilarity
  indices in vegdist or elsewhere, and it can also be
  used to implement many other indices, amongst them, most of those
  described in Legendre & Legendre (2012). It can also be used to
  implement all indices of beta diversity described in Koleff et
  al. (2003), but there also is a specific function
  betadiver for the purpose.
If you want to implement binary dissimilarities based on the 2x2
  contingency table notation, you can set abcd = TRUE. In this
  notation a = J, b = A-J, c = B-J, d = P-A-B+J. 
  This notation is often used instead of the more more
  tangible default notation for reasons that are opaque to me.
With alphagamma = TRUE it is possible to use beta diversity
  notation with terms alpha for average alpha diversity and
  gamma for gamma diversity in two compared sites. The terms
  are calculated as alpha = (A+B)/2, gamma = A+B-J and
  delta = abs(A-B)/2.  Terms A and B are also
  available and give the alpha diversities of the individual compared
  sites.  The beta diversity terms may make sense only for binary
  terms (so that diversities are expressed in numbers of species), but
  they are calculated for quadratic and minimum terms as well (with a
  warning).
Function chaodist is similar to designgist, but uses
  terms U and V of Chao et al. (2005). These terms are
  supposed to take into account the effects of unseen species. Both
  U and V are scaled to range \(0 \dots 1\). They take
  the place of A and B and the product U*V is used
  in the place of J of designdist.  Function
  chaodist can implement any commonly used Chao et al. (2005)
  style dissimilarity:
| 1 - 2*U*V/(U+V) | Sørensen type | 
| 1 - U*V/(U+V-U*V) | Jaccard type | 
| 1 - sqrt(U*V) | Ochiai type | 
| (pmin(U,V) - U*V)/pmin(U,V) | Simpson type | 
Function vegdist implements Jaccard-type Chao distance,
  and its documentation contains more complete discussion on the
  calculation of the terms.
designdist returns an object of class dist.
Chao, A., Chazdon, R. L., Colwell, R. K. and Shen, T. (2005) A new statistical approach for assessing similarity of species composition with incidence and abundance data. Ecology Letters 8, 148--159.
Koleff, P., Gaston, K.J. and Lennon, J.J. (2003) Measuring beta diversity for presence--absence data. J. Animal Ecol. 72, 367--382.
Legendre, P. and Legendre, L. (2012) Numerical Ecology. 3rd English ed. Elsevier
designdist does not use compiled code, but it is based on
  vectorized R code. The designdist function can be much
  faster than vegdist, although the latter uses compiled
  code. However, designdist cannot skip missing values and uses
  much more memory during calculations.
The use of sum terms can be numerically unstable. In particularly,
  when these terms are large, the precision may be lost. The risk is
  large when the number of columns is high, and particularly large with
  quadratic terms. For precise calculations it is better to use
  functions like dist and vegdist which are
  more robust against numerical problems.
data(BCI) ## Four ways of calculating the same Sørensen dissimilarity d0 <- vegdist(BCI, "bray", binary = TRUE) d1 <- designdist(BCI, "(A+B-2*J)/(A+B)") d2 <- designdist(BCI, "(b+c)/(2*a+b+c)", abcd = TRUE) d3 <- designdist(BCI, "gamma/alpha - 1", alphagamma = TRUE) ## Arrhenius dissimilarity: the value of z in the species-area model ## S = c*A^z when combining two sites of equal areas, where S is the ## number of species, A is the area, and c and z are model parameters. ## The A below is not the area (which cancels out), but number of ## species in one of the sites, as defined in designdist(). dis <- designdist(BCI, "(log(A+B-J)-log(A+B)+log(2))/log(2)") ## This can be used in clustering or ordination... ordiplot(cmdscale(dis))#>#> Min. 1st Qu. Median Mean 3rd Qu. Max. #> 0.2733 0.3895 0.4192 0.4213 0.4537 0.5906