Dear Logan,
first of all, I CC HMecology back in, since that way more people can benefit and more can help, too. Couple comments back:
-
What the data are and what a model estimates are two different things. For instance, the RN model takes a binary detection/nondetection response and yields an estimate of underlying abundance. This sounds like magic and often it
works, but sometimes also less well (in the sense of sometimes the resulting abundance estimates make sense and sometimes not). The RN model depends more heavily on its assumptions than does an abundance model that uses more information, such as the binomial
Nmix model for replicated counts or multinomial Nmix for spatially replicated capture-recapture data.
-
What we call TTD models exist both for an underlying abundance- and for an underlying presence/absence state. Trying to estimate abundance from TTD data is more risky than simply estimating presence/absence, again in the sense that
more can go wrong when assumptions are less well met (i.e., estimates can be unreasonable).
-
unmarked function occuTTD() can be used to model either underlying presence/absence or abundance. The change can be effected by chosing linkPsi = 'cloglog' (which yields a model for underlying abundance) or linkPsi = 'logit', which
results in a model for occupancy.
-
About 2000 visits per site for TTD modeling: to be honest I don't even know whether occuTTD() accepts repeated measurements for a closed, or single-season, model. Have to check. If not, may have to go to BUGS software.
Best regards --- Marc
Marc thanks for the response!
I am not necessarily trying to compare RN to TTD estimates. I anticipate likely having to define a visit differently between the two. I am using those two because
Fiss et al. 2024 showed that they work for ARUs and are comparable to N-mixture estimates from human observer point counts. They chose to have their visits sort of match their point count visit structure, which I do not plan on doing. My task is to compare
and contrast the efficiency of ARUs vs human observers for spring monitoring grouse, and I'm hoping to thin the data as little as possible to leverage the temporal strength of ARUs.
I also conducted human observer point counts at my ARU sites and estimated abundance in unmarked's n-mixture function pcount(). I would now like to derive abundance estimates from my ARU data also in unmarked.
I thought RN model response was a simple detection/non-detection per visit?
So for the TTD model you don't foresee any issue with 2,000 visits per site? And time in seconds to the first detection as the response (i.e no binning)?
I will check out the Goldstein paper now.
Really appreciate your response here,
Logan
Dear Logan,
you seem to want to compare the two models for abundance estimation, right ? And you seem to want to process your data identically for both ?
I don't think the latter is necessary. The natural way to get the TTD data is just to take the difference in the time stamps between first detection and start of recording. There is no need to bin here; this would just lose accuracy.
However, for a method that uses discrete-time detection data, such as the classical RN model, you have to make the usual choice of what consists an occasion. In making this choice, you must balance the wish to not lose information
(which happens when you have more than 1 detection during an occasion, but that then gets recorded as a 1) on the one hand, and to not have too many occasions on the other, for numerical reasons, and because a too fine temporal discretization may lead to problems
with temporal autocorrelation in the detections. For ideas about how to discretize continuous recording data, see the
recent paper by Goldstein et al.
Best regards — Marc