To let evaluations with before studies, i and used nonspatial need-recapture remedies for estimate adult jaguar occurrence (look for Appendix B to own methods and you can show).
We estimated densities alone for men, reproductive women, and you will nonreproductive women. We attempted to match patterns directly to observations away from cubs, however their sparse simply take records did not give enough investigation getting a max probability study. In order to estimate cub thickness, we increased the reproductive women density from your finest model of the mean level of cubs per reproductive females. Such rates greet calculation from overall jaguar density and populace build for males, nonreproductive ladies, reproductive ladies, and cubs.
The complete testing energy are a dozen,302 cam trap-night. We obtained 1465 grabs, together with 1369 having identifiable people (Table step one). Altogether, i known 42 jaguars, including fourteen males, 14 mature female, and you can fourteen cubs. Of fourteen shoot adult lady, eight had been positively recreating and you can photographed which have cubs (Pictures D1, D2). Although we joined equivalent quantities of people, female, and you will cubs regarding data area, the latest grab regularity of each category differed: 58% away from recognized pictures were the ones from guys (798 catches), 33% out-of identifiable captures was in fact those of women (452), and simply 9% was the ones from cubs (119). An average of, boys were grabbed 56 moments for each and every, lady thirty-two minutes, and you will cubs only 9 times. Reproductive females got slightly highest total number of captures than just nonreproductive lady (257 versus 195, respectively) and higher mediocre number of catches for every single private (38 as opposed to 28). Reproductive lady was more frequently seized by yourself (109 times) than followed by cubs (69 captures) throughout known kiddies dependence. However, cubs was basically recorded more often the help of its mothers (83 personal captures) than by yourself (thirty-six catches).
Of the 32 models analyzed with the secr package with sex/reproductive status and sessions as covariates, those which did not allow density to vary across sessions obtained the lowest AICc values. In contrast, models assuming density variation across sessions received less support (Tables 2, C1). The top secr model for adult jaguars included an effect of sex/female reproductive status on D, ? 0, and ? and between session variation in ? 0. All three parameters differed significantly between sex/reproductive status groups (Table 3). Baseline detection probability was lowest for reproductive females (0.04 on average), whereas nonreproductive females had the greatest baseline detectability (0.13 on average) and males intermediate (0.08 meet austrian women on average) to the two female reproductive classes. Males had the largest values of estimated movement distribution (? = 2.97 ± 0.09 km), while reproductive and nonreproductive females obtained smaller ? values (2.04 ± 0.11 and 2.32 ± 0.19 km, respectively). Estimated densities were higher for reproductive females and males (1.97 ± 0.33 and 1.62 ± 0.22 individuals/ 100 km 2 , respectively) than for nonreproductive females (0.85 ± 0.19 individuals/100 km 2 ). In total, the best model estimated 4.44 ± 1.16 adult jaguars/100 km 2 (Table 3).
Regarding observations of your own 7 reproductive girls which have kiddies when you look at the data several months, i estimated 1.64 cubs per reproductive women typically. Additionally, one cub was filed alone on a single celebration along with an unidentified mother. We omitted this lone observance out-of next analysis. On the basis of reproductive people occurrence regarding most useful design, we projected step 3.23 cubs/one hundred kilometer 2 regarding the analysis area. Therefore, we projected a total density out of seven.67 jaguars/100 km 2 . Jaguar population design is actually 21% adult males, 11% nonreproductive girls, 26% reproductive female, and you can 42% cubs (Dining table step 3).