Thanks for the comments awhile back. I have come up with some more
questions/concerns that I hope you can help me with.
Here is the summary you wanted to see:
> summary(grye.abun)
unmarkedFrame Object
270 sites
Maximum number of observations per site: 6
Mean number of observations per site: 3.42
Sites with at least one detection: 30
Tabulation of y observations:
0 1 2 3 4 5 6 7 8 10 11 15 <NA>
883 21 7 2 1 2 1 1 1 1 2 1 697
Site-level covariates:
season vegetation.class plot
F:153 A: 89 L: 98
S:117 B:106 M:114
D: 38 N: 58
E: 37
>
…………
regarding treatment of season…..
Maybe I am not dealing with this properly. I have Spring and Fall, and
would like to look at both abundance and detectability in each season,
at each of the plot*vegetation.class combinations. My set-up is
this….I have 270 ‘sites’ which are transects. Each of these ‘sites’
have up to 6 ‘visits’- which are separate point counts completed in
the same day. 153 of the ‘sites’ were visited in the Fall, and 117 in
the Spring . I was going with pcount because my ‘visits’ definitely
occur within closed population, but maybe not? Should I be using
pcountOpen in a migration survey situation?
--------
I did use the predict() to show abundance at each
plot*vegetation.class combination. I have read many threads, and I am
wondering if I am interpreting these predicted numbers correctly. Is
1.65397 the estimated mean density at Plot L, Veg A ? This number does
seem accurate from what I saw during surveys.
> new.pred=predict(grye.abun.global, newdata=new.data, type="state")
> temp=data.frame(plot=newplot,veg=newveg, est=new.pred$Predicted, SE=new.pred$SE, l95=new.pred$lower, u95=new.pred$upper)
> temp
plot veg est SE l95 u95
1 L A 1.65397289 0.39550502 1.03510751 2.6428427
2 L B 1.77604147 0.43172772 1.10290832 2.8600050
3 L D 0.47121677 0.22610536 0.18398658 1.2068557
4 L E 0.43670425 0.23315824 0.15336538 1.2435049
5 M A 1.27118367 0.32515513 0.76998116 2.0986331
6 M B 1.36500117 0.31010597 0.87448816 2.1306500
7 M D 0.36216015 0.17507513 0.14041503 0.9340879
8 M E 0.33563507 0.17781203 0.11882822 0.9480147
9 N A 0.31576743 0.15397029 0.12142715 0.8211431
10 N B 0.33907209 0.16220366 0.13276952 0.8659358
11 N D 0.08996212 0.05772674 0.02557774 0.3164151
12 N E 0.08337318 0.05591909 0.02239331 0.
3104091
However, the estimates of detection are WAY to low.
This is of concern, because the detections are very low…. I was
surveying 100m radius area on a mudflat. My detection of a greater
yellowlegs in the field should be very close to 1, if not 1; whereas
detection is showing 0.07 for spring, and 0.23 for fall. (if I
interpret that correctly)
> plogis(coef(grye.abun.global, type="det"))
p(Int) p(seasonS)
0.23487372 0.07275806
Maybe I am calculating the detection incorrectly?
I wonder if low detection in pcount (but shouldn’t be in actual
survey) has something to do with these species being gregarious, and
the ‘high’ counts of 10, 11, 15, etc may correlate with flocks
(clusters). As of a June 2010 thread, cluster size was not a part of
unmarked. Has this changed?
Also- there was a thread on schooling coho salmon and concern on non-
independence. Because shorebirds may be in small flocks (2-15 on my
field site) during migration, maybe I am seeing this with my data?
i.e. do I need to think about non-independent detection (Martin et
al. 2011), and possibly looking at a beta-binomial mixture model as
opposed to N-mixture model?
maybe pcount is not best to use for estimating abundance/detection on
migrating shorebirds in 2 different seasons.
Thanks for any thoughts. I am concerned I may have an overestimation
of abundance, and of all the things I have read, I am not sure what
exactly could be my problem.