null models with continuous abundance data

On 07/01/2010 21:48, "Etienne Lalibert?" <etiennelaliberte at gmail.com> wrote:

Many thanks again Carsten.

Yes, you're right that care must be taken to

ensure that a decent number

of unique random matrices must be obtained. I

don't think it would be a

problem in my case given that transforming my

continuous abundance data

to count by

mat2<- floor(mat * 100 / min(mat[mat >

0]) )

can quickly lead to a very large number of individuals (hundreds

of

thousands if not > million in some cases). The issue then becomes

mostly

one of computing speed, but that's another story.

Following your

suggestion, I came up with a simple (read na?ve) R

algorithm that starts with

a binary matrix obtained by commsimulator

then fills it randomly. It seems to

work relatively well, though it's

extremely slow.

In addition, because the

algorithm fills the matrix one individual at a

time, I sometimes ran into the

problem of one individual which had

nowhere to go because "ressources" at the

site (i.e. the row sum) was

already full. In that case, this individual

disappears, i.e. goes

nowhere. This is a bit drastic and clearly sub-optimal,

but it's the

only way I could quickly think of yesterday to prevent the

algorithm

from getting stuck. The consequence is that often, the total number

of

individuals in the null matrix is a bit less than total number

of

individuals in the observed matrix.

Etienne,

This is the same problem as filling up a binary matrix: you get stuck before
you can fill in all presences. The solution in vegan::commsimulator was
"backtracking" method: when you get stuck, you remove some of the items
(backtrack to an earlier stage of filling) and start again. This is even
slower than initial filling, but it may be doable. The model application of
backtracking goes back to Gotelli & Entsminger (Oecologia 129, 282--291;
2001) who had this for binary data, but the same idea is natural for
quantitative null models, too. The vegan vignette discusses some details of
implementation which are valid also for quantitative filling.

I would like to repeat the serious warning that Carsten Dormann made: you
better be sure that your generated null models really are random. P?ter
S?lymos developed some quantitative null models for vegan, but we found in
our tests that they were not random at all, but the constraints we put
produced peculiar kind of data with regular features although there was
technically no problem. Therefore we removed code worth of huge amount of
developing work as dangerous for use. I do think that also the r2dtable
approach is more regular and less variable (lower variance) than the
community data, and you very easily get misleadingly significant results
when you compare your observed community against too regular null models.
This is something analogous to using strict Poisson error in glm or gam when
the data in fact are overdispersed to Poisson. Be very careful if you want
to claim significant results based on quantitative null models. Would I be a
referee or an editor for this kind of ms, I would be very skeptical ask for
the proof of the validity of the null model.

Cheers, Jari Oksanen

I don't see this as being a
real

problem with the large matrices I'll deal with though, but

definitely

something to be aware of.

If you're curious, here's the simple

algorithm, as well as some code to

run a test below. I'd be very interested to

compare it to Vazquez's

algorithm!

Thanks again

Etienne

###

nullabun <-

function(x){

? require(vegan)
? nsites <- nrow(x)
? nsp <- ncol(x)

rowsum <- rowSums(x)

? colsum <- colSums(x)
? nullbin <- commsimulator(x,

method = "quasiswap")

? rownull <- rowSums(nullbin)
? colnull <-

colSums(nullbin)

? rowsum <- rowsum - rownull
? colsum <- colsum - colnull

ind <- rep(1:nsp, colsum)

? ress <- rep(1:nsites, rowsum)
? total <-

sum(rowsum)

? selinds <- sample(1:total)
? ? ?for (j in 1:total){

indsel <- ind[selinds[j]]

? ? ? ? sitepot <- which(nullbin[, indsel] > 0)

if (length(ress[ress %in% sitepot]) > 0 ){

? ? ? ? ? ?sitesel <-

sample(ress[ress %in% sitepot], 1)

? ? ? ? ? ?ress <- ress[-which(ress ==

sitesel)[1] ]

? ? ? ? ? ?nullbin[sitesel, indsel] <- nullbin[sitesel, indsel]

+ 1

? ? ? ? ? }
? ? ?}
return(nullbin)
}


### now let's test the

function

# create a dummy abundance matrix
m <-

matrix(c(1,3,2,0,3,1,0,2,1,0,2,1,0,0,1,2,0,3,0,0,0,1,4,3), 4,
6,

byrow=TRUE)

# generate a null matrix
m.null <- nullabun(m)

# compare

total number of individuals

sum(m) #30
sum(m.null) #29: one individual got

"stuck" with no ressources...

# to generate more than one null matrix, say

999

nulls <- replicate(n = 999, nullabun(m), simplify = F)

# how many unique

null matrices?

length(unique(nulls) ) # I found 983 out of 999

# how many

individuals in m?

sum(m) # there are 30

# how bad is the problem of

individuals getting stuck with no ressources

in null matrices?
sums <-

as.numeric(lapply(nulls, sum, simplify = T))

hist(sums) # the vast majority

had 29 or 30 individuals

Le jeudi 07 janvier 2010 ? 10:34 +0100, Carsten

Dormann a ?crit :
Hi Etienne,

I'm afraid that swap.web cannot easily
accommodate this constraint.
Diego Vazquez has used an alternative approach
for this problem, but I
haven't seen code for it (it's briefly described in
his Oikos 2005
paper). While swap.web starts with a "too-full" matrix and
then
downsamples, Diego starts by allocating bottom-up. There it should be

relatively easy to also constrain the row-constancy of connectance.

I
can't promise, but I will hopefully have this algorithm by the end
of next
week (I'm teaching this stuff next week and this is one of the
assignments).
If so, I'll get it over to you.

The problem that already arises with
swap.web for very sparse matrices
is that there are very few unique
combinations left after all these
constraints. This will be even worse for
your approach, and plant
community data are usually VERY sparse. Once you
have produced the
null models, you should assure yourself that there are
hundreds
(better thousands) of possible randomised matrices. Adding just
one
more constraint to your null model (that of column AND row constancy

of 0s) will uniquely define the matrix! Referees may not pick it up,
but it
may give you trivial results.

Best wishes,

Carsten


V?zquez,
D. P., Meli?n, C. J., Williams, N. M., Bl?thgen, N., Krasnov,
B. R., Poulin,
R., et al. (2007). Species abundance and asymmetric
interaction strength in
ecological networks. Oikos, 116, 1120-1127.

On 06/01/2010 23:57, Etienne
Lalibert? wrote:

Many thanks Carsten and Peter for your suggestions.

commsimulator indeed respects the two contraints I'm interested in, but>
only allows for binary data.

swap.web is *almost* what I need, but

only overall matrix fill is kept

constant, whereas I want zeros to move

only between rows, not between

both columns and rows. In others words, if

the initial data matrix had

three zeros for row 1, permuted matrices

should also have three zeros

for that row.

I do not doubt that

Peter's suggestions are good, but I'm afraid they

seem a bit overly

complicated for my particular problem. All I'm after

is to create n

randomly-assembled matrices from an observed species

abundance matrix to

compare the observed functional diversity of the

sampling sites to a null

expectation. To be conservative, this requires

that I hold species

richness constant at each site, and keep row and

column marginals fixed.

Could swap.web or permatswap(..., method = "quasiswap") be easily

tweaked to accomodate this? The only difference really is that matrix

fill

should be kept constant *but also* be constrained within rows.

Thanks

again for your help.

Etienne

Le 7 janvier 2010 08:17, Peter

Solymos <solymos at ualberta.ca> a ?crit :

Dear Etienne,

You can try the Chris Hennig's prablus package which have a parametric

bootstrap based null-model where clumpedness of occurrences or

abundances (this might allow continuous data, too) is estimated from

the

site-species matrix and used in the null-model generation. But

here, the

sum of the matrix will vary randomly.

But if you have

environmental covariates, you might try something more

parametric. For

example the simulate.rda or simulate.cca functions in

the vegan package,

or fit multivariate LM for nested models (i.e.

intercept only, and with

other covariates) and compare AIC's, or use

the simulate.lm to get

random numbers based on the fitted model. This

way you can base you

desired statistic on the simulated data sets, and

you know explicitly

what is the model (plus it is good for continuous

data that you have).

By using the null-model approach, you implicitly

have a model by

defining constraints for the permutations, and

p-values are

probabilities of the data given the constraints (null

hypothesis), and

not probability of the null hypothesis given the data

(what people

usually really want).

Cheers,

Peter

P?ter S?lymos

Alberta Biodiversity Monitoring Institute
Department

of Biological Sciences

CW 405, Biological Sciences Bldg
University

of Alberta

Edmonton, Alberta, T6G 2E9, Canada
Phone:

780.492.8534

Fax: 780.492.7635



On Wed, Jan 6,

2010 at 2:18 AM, Carsten Dormann <carsten.dormann at ufz.de> wrote:

Hi Etienne,

the double constraint is observed by two

functions:

swap.web in package bipartite

and

commsimulator in vegan (at least in the r-forge

version)

Both build on the r2dtable approach, i.e. you have,

as you propose, to turn

the low values into higher-value integers.

The algorithm is described in the help to swap.web.

HTH,

Carsten

On 06/01/2010 08:55, Etienne Lalibert? wrote:

Hi,

Let's say I have measured plant biomass for a total of 5

species from 3

sites (i.e. plots), such that I end with the

following data matrix

mat<- matrix(c(0.35, 0.12, 0.61, 0,

0, 0.28, 0, 0.42, 0.31, 0.19, 0.82,

0, 0, 0, 0.25), 3, 5, byrow =

T)

dimnames(mat)<- list(c("site1", "site2", "site3"),

c("sp1", "sp2",

"sp3", "sp4", "sp5"))

Data is

therefore continuous. I want to generate n random community

matrices

which both respect the following constraints:

1) row and

column totals are kept constant, such that "productivity" of

each

site is maintained, and that rare species at a "regional" level

stay

rare (and vice-versa).

2) number of species in each plot

is kept constant, i.e. each row

maintains the same number of zeros,

though these zeros should not stay

fixed.

To

deal with continuous data, my initial idea was to transform the

continuous data in mat to integer data by

mat2<-

floor(mat * 100 / min(mat[mat> ?0]) )

where multiplying

by 100 is only used to reduce the effect of rounding

to nearest

integer (a bit arbitrary). In a way, shuffling mat could now

be seen

as re-allocating "units of biomass" randomly to plots. However,

doing so results in a matrix with large number of "individuals" to

reshuffle, which can slow things down quite a bit. But this is only part

of the problem.

My main problem has been to find an

algorithm that can actually respect

constraints 1 and 2. Despite

trying various R functions (r2dtable,

permatfull, etc), I have not

yet been able to find one that can do

this.

I've had some kind help from Peter Solymos who suggested that I try the

aylmer package, and it's *almost* what I need, but the problem is that

their algorithm does not allow for the zeros to move within the

matrix;

they stay fixed. I want the number of zeros to stay constant

within each

row, but I want them to move freely betweem columns.

Any help would be very much appreciated.

Thanks

--
Dr. Carsten

F. Dormann

Department of Computational Landscape Ecology

Helmholtz Centre for Environmental Research-UFZ

Permoserstr. 15

04318 Leipzig

Germany

Tel: ++49(0)341 2351946

Fax: ++49(0)341 2351939

Email: carsten.dormann at ufz.de

internet: http://www.ufz.de/index.php?de=4205

--
Etienne

Lalibert?

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