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This species is encountered in Kokrajhar town of Assam, India. It is thin walled bamboo. As per my knowledge it seems to be Schizostachyum sp. I request the peers to kindly help me identify the same.
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It looks difficult to reach any conclusion from the above posted pictures.
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Hi everybody,
we are using circular pitfall traps (regular yogurt cups) since many years, and unfortunately, sometimes we encounter mice and lizards as by-catch in our samples.
These animals fall in the pitfall traps, are not able to climb out of it and drown...
Researches (e.g. see link attached) and personal reflections resulted in the following possible easy-to-install preventive measures:
1) covering the pitfall traps with a thin, wide-meshed iron grid, so it is too thin to "grab and climb" for invertebrate, but slippery enough for insects and spiders
2) using funnels with a slippery surface, so small vertebrata can't enter, while insects can fall into it
I personally like more solution 1, but I wanted to ask you to share your experience :-)
We aim mostly on spiders, centipedes, millipedes, beetles and other surface insects.
Thank you and greetings,
Michael
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I recently began to work with viviparous Neotropical skinks of the genus Mabuya. Specifically with females at different stages of gestation. My tutor and lab colleagues have studied them for a long time and a recurring comment is related to the difficulty of field sampling.
The standard method of catch is by hand, but these lizards are very quick moving through the litter, and their smooth-scales covered skin makes them difficult to hold. Also, in the most advanced stages of pregnancy, these lizards stops feeding so funnel traps will likely be less effective.
I have little experience in catching, and I am planning some field trips to obtain some specimens (especially to learn about the field work). I would like to try different catch methods, hoping to make it easier to obtain research material.
I will be very grateful for any suggestions or advice you can provide.
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Artificial retreats :)
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Hi folks,
I've been googling around for quite some time trying to find papers pertaining to pilot studies on ecological/wildlife/biodiversity assessment research, but with little success. Most of them pertain to medical research only. Shall be grateful.
Thanks
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I'm in the process of buying new equipment to record the vocalizations of wild mammals, and have used Marantz's solid state recorders with great success in the past. However, it seems that their PMD range of recorders are not easily available anymore. I've looked around and the Tascam DR-1 portable solid state recorder seems like a good option, but I have no experience with that product.
I'd appreciate any advice on the best, portable recorders to be used in the field. Nothing too fancy (I don't expect ultrasonic vocalizations, for example), but I'd love to hear from you about the pro's and cons of different recording tools that you've used. I would need the recordings to be of good enough quality to analyze properly in programs like AviSoft.
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Hi Alina,
I have used many recorders throughout my career and it wasn't until I discovered the Sound Devices Model 722 that I stopped buying other field recorders. It is a two-channel digital recorder (they also make a 4-channel model), made in the US, with a wide, flat frequency response that enables you to record up to the high-frequency limit of your microphone. So if we want to record ultrasound, we use an ultrasonic microphone. If we don't need this capability, we use a standard directional mike that drops off at 18 kHz or so. The microphone signal is digitized at a sampling rate selected by the user via a menu. The digitized signal is stored as a .wav file on the internal compact flash card. When this is filled, you can easily transfer the contents of the CF card to the internal 40 GByte hard drive. This is a small, lightweight recorder that can run on rechargeabale batteries that give a recording time of 6-12 h. Take a look at their website- I think you will be pleased. By the way, I have no connection to this company!
Hope this helps-
Peter
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I have a long-term slow loris research project. We have been using the very expensive Biotrack Sika and six element yagi. Unfortunately, despite working in a non-arduous anthropogenic landscape and keeping equipment clean and dry (although it rains frequently), the break downs have become financially non-viable and we are looking for a more commercial radio receiver that is more affordable. I used Icom in the past but they seem largely discontinued. Does anyone have any experience with Uniden? It is to track small animals within a few km at a frequency of about 150. Key is cost efficiency as our project budget is very low!
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You could have a look at the work that Dr Debbie Saunders has done with a custom receiver mounted on a drone. Tracks up to 100 animals simultaneously in real time, creates a high point.
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Nowadays, CRISPR take a lot of attention as new revolution in biology, on another hand we have some hot topics such as antibiotic resistant, nanobiotechnology (hydrogels and drug delivery) and imaging development technologies etc.
So tell me your opinion about the next revolution in biology? (considering of all fields of biology)
And are we ready for that?
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I am looking into the assemblages of Silphidae between different habitats and within each habitat as well.
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I have about the same experience in this with Fabian. In my work ''Seasonal variation of the insect fauna in hedgerows and cereal fields in the area of Elassona, Larisa'' (in Greek), in pitfall traps with small dead mice and turtles (accidentally fallen into them), I caught hundreds of Silpha tristis (= granulata) and Aclypea undata (= Blitophaga undata), plus some Nicrophorus.
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I'm currently looking for modern field techniques in catching wrasses and would like suggestions or tips, as some papers that I have read can be quite vague with their capture process (i.e., tools used, technique, processing). One paper that caught my attention was by Worachananant et al. (2016), but their capture process was also vague despite the wide range of tools used in the study. Any suggestions or recommended literature are greatly appreciated. Thanks in advance!
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Hi Kent,
If you are interested in capturing live specimens with non-destructive methods then your best bet is to use traps/pots and/or suction (or slurp) guns. We also found that small nets made of clear plastic were very useful in capturing small wrasses on coral reefs. One of the best ways to capture small wrasses on reefs is with slurp/suction guns made of transparent acrylic. Papers that use these collecting techniques usually do not describe in detail how they have actually built their collecting devices. If you go to Google Scholar and search for some of these terms you’ll find a lot of information. You may find these of some help:
Slurp or suction guns:
Tomas
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I am looking to track within breeding season movements of a 25 g bird. The species is not philopatric, so trackers that require recapture are not an option. Trackers must be under 0.75 g per USGS regulations. I'm thinking I am going to be limited to radio transmitters but if you know of other options, I would be very interested. Do you have a favorite radio transmitter brand? Cost is a major consideration. Thank you!
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First of all you have to ask some questions. How far do the birds range in the time you want to track them? How many do you want to track at once? Will you be flying or monitoring from a car/truck? If you have funding for air, this is the best if the birds are either migrating or moving around with no roost to return to. I tracked migrating western sandpipers (about 25g) using Lotek transmitters and receiver. These are coded radios so that you only have one frequency, saving you time circling around and around to make sure that your receiver has cycled through all of the frequencies.
However, I had problems with detection of the devices at first, but I believed that they straightened that out. The receiver records the entire time so if you are distracted by something and forget to write down one of the codes, it's all there for you in the receiver.
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We will photograph feedings of birds (Great tits and also Barn owls) by nest boxes with camera traps to know who, what and when they bring a prey in. A PIR sensor is not working well enough during tests (Bushnell Agressors and Reconyx HC500 are tested). They missed to much events of the well isolated birds. The birds has pit tags, but that system failed +-10%. And that could be the clue of the research...
By that I was thinking to connect a simple and less energy consuming IR beam on a trail cam like this one: http://eltima.de/jokie-179/product/jokie2.html?details=features-180
I can also connect DSLR's on the IR beam, but that is most times not so easy to install and to much disturbance for barn owls.
I know the Reconyx PC-series can work with an external sensor as trigger with a special cable, but that price is (a bit) far above budget. (http://images.reconyx.com/file/Professional%20Settings%20User%20Guide.pdf)
Now I tried to connect a IR port on a Bushnell E2. But how can I switch of the PIR sensor? And where to solder the port for IR beam on? An extra plug is easy to install, but the input of the PIR is horrible to find...
Are there maybe some others who have experience with connecting trail cams on a IR barrier? Or maybe are there other brands that have also this option?
I like to come in contact with them and like to share experiences in this.
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For monitoring inside nest boxes I recommend CCD camera with a standalone mini DVR, see attached paper.
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Hello all,
I am a hardcore experimental biologist. In particular, I am well-versed in molecular and cell Biology techniques. However, the area of Bioinformatics and Computational Biology have revolutionised the field of Biology. 
Can anyone suggest basic hands-on-trainings/courses of international standard where we can get a good exposure on the following for beginners?
1. Bioinformatics
2. Systems Biology
3. Synthetic Biology
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Hi,
Please check the following links. There are wonderful courses that are free, ranging from absolute beginners to advanced courses.
I would suggest getting started with learning to program in Python, this is fast becoming the go-to scripting language for bioinformaticians and systems biologists worldwide.
Good luck,
Ratnadeep
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We will start soon a 1 year (at least) camera trap project, where the main target will be mesocarnivores. Unfortunately, some animals like mongooses don´t have spots or truly individual marks and many pictures might be blurred, especially at night.
The idea is to use tags (e.g. hear tags, hair cuts, etc.) that will increase the chance of individual identification, even in worst conditions!
At the same time, we will be conducting box trapping sessions to capture several individuals.
Can someone suggest any easy and durable method to mark animals with the lowest impact possible?
Thanks a lot in advance
Best Regards
Filipe Carvalho
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Hi,
In my experience, there is not a good way to mark the animals like mongoose. Hair cuts are temporal, and not very useful. Hear tags would be great, but they come off very soon. Maybe the best way is a plastic collar with geometrical marks. In this paper I've used spatial counts and I've marked (telemetry tag) only one Egyptian mongoose, but was enough to estimate the density.
Best,
Jose
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We want to monitor nest and ambient temperature on the tundra, but have just been informed that they have again delayed our order and it won't arrive until AFTER our field season.
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Hi Melanie,
Bummer about the ibuttons. I worked with a Canadian company some years ago that sell loggers that should meet your needs. The company is Alpha Mach (alphamach.com). They were very responsive and had some high quality products. I think what I used were called ib-krill tags. They also now have what is called a WeeTag--these are RF&RFID temperature loggers; I've wanted to try these at some point.
Good luck to you! Are you in AK now? I leave for AK tomorrow...
Loren
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I'm planning a transect study using plasticine caterpillars and would like to take pictures in the field to document signs of predation, prior to transporting back to the lab.
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Olloclip Macro Pro Lens is pretty good for 7x, 14x and 21x macro. These cost ca.  £80 in the UK. 
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Are pan traps more effective if coated with ultraviolet reflective paint? If so, what brands do people use or recommend? We have found these:
Any advice or thoughts welcome.
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The patterns of abundance will be different in UV vs. non-UV painted pan traps, but you are likely to get the same genera. Our colleagues in N-America had similar results!
On the question of different colours, see the Venn diagram below based on our surveys in Belgium.
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Hi everyone
We would like to use trail cameras to record the behaviour of small carnivores at night. No need to say that we have a limited budget. The latest entry-level Bushnell model (Essential E2) does not allow to take video-clips longer than 15 s at night with 3 s trigger interval, whereas the Essential allowed up to 1 min with 1 s interval (this is what we call progress...). We are therefore looking for cheap but reliable alternatives. I found good reviews on the Bestguarder DTC-880V/SG009:
N.B. Apparently this model (or a slightly modified version) is also marketed under other brand names such as TEC.BEAN (and maybe XIKEZAN).
I also read some positive feedbacks from buyers on Amazon but noticed that a few people mentioned that the nocturnal video-clips and pics were not necessarily of good quality (i.e. "grainy").
We were wondering whether any of you have used this trail camera and if so, what is your opinion on/assessment of the quality of nocturnal video-clips?
Also, do you have any feedback on the reliability of this brand(s)/model(s)?
Thanks in advance for your precious assistance.
Emmanuel
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Hi Emmanuel
Small carnivore behaviour is a specialist and challenging application where nobody has done much camera trapping - the big markets are deer hunters in the USA and researcher want still pictures to do population estimates. There are some papers from Australia and New Zealand, and recent papers on interspecific scent marking, in Santa Cruz, Panama and Botswana that I can send you if you have not seen them already.
I have done some small carnivore camera trapping with mixed results. In my experience the most important feature is trigger speed - at ranges where the image of a small carnivore is a sensible size; out to about 5 or 6 m from the camera, a 1 s trigger delay, added to PIR sensitivity being lower at the edges of the detection zone means that videos begin with the animals already leaving the field of view. Fortunately faster triggers (0.5s) are now standard. If you want to record behaviour that goes on for a while you need long videos (with the disadvantage that they chew memory and take along time to review) and a fast recovery between videos or sod's law will determine that the camera will miss the critical bit !.
Among older cameras Bushnell Trophycams struggle with detection when it is hot, and the video quality is marginal. Stealthcams are way too slow.
Reconyx Ultrafires produce very good videos for a very high price, and have a slow response and recovery. Spypoint 11Ds, at abut 1/3 the price of the Reconyx have very fast triggers and recovery, but their video is not as good. Browning have three new models out that look interesting. Their Strike Force Elite HD is mid range with mid range perfomance but seemed to have a dead spot about 5m out.
Putting it diplomatically; the two review sites you link are not as objective as could be wished.The most reliable reviews are those of TrailcamPro's site; http://www.trailcampro.com/, but even they too are in the business of selling trail cameras, so they tend to look on the bright side.
There is a sudden explosion of mid-range camera traps like the on you are considering. It is likely that they are being produced by the same Chinese manufacturers as make the established brands, so in principal there is no reason why they will not work as well as the established brands. What I do notice is that the price on Amazon is about the same as for Bushnell's, Brownings and Spypoints with similar performance, so you are not saving money by going for a new brand.
They quote a very long detection range, but they could have achieved it with a nice cold background and a large target like a human. It is not relevant to recording small carnivores against a hot African background, - I have seen a family of Selous mongoose playing for 5 min or so 4 m from a Bushnell Trophycam (the old model) in the early evening with not a single image captured !! At 20 m a small carnivore will be a tiny speck anyway, especially with the 90 degree field of view. Unless there is autoexposure control, very bright IR lights are actually a drawback for small targets close up because all you get is burned out images. 
Price and performance specifications are not good predictors of actual performance in the field - you really need to try out an actual camera, but that gets very expensive very quickly. It would be encouraging if the suppliers had enough faith in their products to make them available for testing for research applications.
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At times I catch 2000+ mosquitoes in a CO2 baited trap. I would like to get an idea of the population without identifying and counting every mosquito.  What sampling methods are appropriate? I have been quartering the pile and multiply the results by 4, but is there a better way? And is there a sample size (sample size formula) I can use to ensure I have a large enough sample to accurately represent the trap population?
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Thank you very much for your response.
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I am interested in how to classify activity measurements from GPS collars for kangaroos.
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Thanks Wendy
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Clip cages are used in laboratories for biology determination of insects. Can anyone please tell me the best way to find out the biology of small insects like wheat aphids in the field condition?
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Pl.read the materials and methods of the article attached. The yellow sticky trap was used. You can use any sticky material like, castor oil. Count  randomly at 10 places in the  trap using  1 X 1  inches cut space in acrylic  sheet  of  3x3 or 4x4 or any bigger size acrylic sheet .Take the average and multiply by the total exposed area of the yellow trap. I hope it may help you. 
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Seeking alternatives to a Cessna 172 aircraft capable of being fitted with VHF antennae to complete radio-tracking surveys in remote terrain. Ideally I am looking for examples of successful use of twin-engine, turbine aircraft.
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I've spent a major portion of my career as an ungulate researcher in the Pacific Northwest of the United States radio-tracking ungulates from aircraft. Sergio and the others provide some useful information.  It is important that you match the aircraft and it's performance capabilities to the terrain and elevation of your study area.  Personally, I would suggest a Piper Super cub, M-7 Maule, Cessna 180, 182, or 185 as suitable single engine aircraft for telemetry work.  When flying in extremely mountainous with very limited options for landing in the event of an engine failure, I prefer a Cessna 336 or 337 if available; these aircraft perform like a 182 and will bring you home on one engine.  Pilot experience in conducting aerial telemetry and mountain flying cannot be over-stated.
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I'm using GPS coordinates for a particular species and need to enter this data into a database. Unfortunately, some of the researchers collecting the data did not record the GPS error. I am wondering if it makes sense to estimate error in those cases for entry into a database or if I should leave the GPS error field blank? Are there any publications or sources touching on this issue that anyone knows about?
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The error depends on the type of GPS  and the observational period... So, your GPS is single or dual-frequency ? You can browse this publication ( http://www.asprs.org/a/publications/pers/2001journal/september/2001_sep_1021-1026.pdf especially Table 2 ) and you will find the accuracy of GPSs ( Both Signle and dual-frequency ). If it does not enough for you, please explain your problem in more details.
PS : Why do you need GPS errors data ? Will you use them in the study ? If not, I think you can leave the field blank.
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I'm working on Flying-foxes monitoring and I want to know how I can built my protocol of fly-out count.
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Hi Malik,
all bat colonies may change in numbers from day to day (bats can switch between roosts) and of course two replicates/month, say, would give you a better idea of how many individuals are there, but overall if your aim is to have a year-round picture of colony size I would say that one count per month will suffice and rather concentrate on having a complete set of (single) monthly counts. 
All best
Danilo
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I have seen that determination of age by teeth analysis is possible ...
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Hi,
You can measure the weight and the length of the forearm to determine the age (whether adult or Juvenile).
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A student in a course with me has data on noxiously abundant flies
near a mink farm. Fly abundance was obtained monthly
at 8 equally spaced trap locations along 3 transects,
each within a narrow strip with a different treatment
(control, manure, manure + offal).
Clearly treatment and experimental unit (strip) are confounded.
It occurred to me that useful information might be obtained by
blocking at right angles to the strips, depending on the spatial
autocorrelation. The strip separation is the same as the trap
separation along a strip.
The within strip acf crosses from positive to zero at a lag of
around 3. Which suggests blocking the trap data at either end
of the parallel strips (two blocks, conservative).
Or perhaps even 3 blocks (either end and middle).
Does anyone have a reference on acf to post-stratify data?
Several google searches, nothing relevant
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Dear Doctor,
Please find attached a document relative to "spatial auto-correlation".
Have a nice day.
A.B. 
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I plan on using fecal samples to identify individuals within the study area. Within each grid cell I was planning on rather opportunistically hiking in good habitat, along animal paths, etc. As long as the effort is even across grid cells I am hoping that capture/recapture models will be effective? Concerning grid size, I know that probability of recapture is important, so is basing the cell size on the species' typical home range size appropriate? Thanks.
Edit/Update: Additional Info - 
I am planning on conducting this research on giant pandas on a pretty small scale (focusing on the borders of Wolong Nature Reserve, perhaps with a 3km buffer on either side). Other research (telemetry studies) has resulted in an average home range size of about 7 square km in this area, using minimum convex polygon (MCP) methods. There is also pretty high spatial overlap in this species. So far I have been considering grid cells of 2.25 square km to ensure effective coverage (the terrain is extremely difficult), which would also result in a grid 2 cells deep on each side of the reserve, keeping with the 3km buffer.
On the other hand, perhaps this increases the chances of unneeded recaptures and the cell size could be increased to around 7 square km? This would also save greatly on time, which is a consideration. I am not sure which is more effective and what the trade-offs are when considering modelling/statistical analysis of the data later.
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Whoops, thought I'd answered.  Tom, I think the reference you should look at (beyond the Royle et al. 2014 book chapter dealing with area searches) is by Thompson et al. 2012 in JWM (something like a framework for SCR with unstructured sampling, involves scat-detecting dogs).  You also might look at Murray Efford's 'secr' vignettes for area searches or transect searches.  These will be the most trustworthy sources. 
In short, I think the grid cell must be smaller than a home range.  in a traditional area search (e.g., the Royle and Young 2008 paper), the (single) cell is being exhaustively systematically searched, so that the sampling allows for (imperfect) animal detection essentially anywhere.  In your situation, you are sampling along a one dimensional-transect or route, and animals can only be detected along that route.  For a number of reasons, transect-based samples or linear routes cause some difficulty related to the continuous space being sampled. One way of dealing with this is to treat the center of a grid cell as something like a static camera or hair-snag; if this is the route you follow, then you want grid cells smaller than a home range so that you actually generate spatial recaptures!  My memory is that the guidelines were something like 1-2 x sigma for cell dimensions, but check the references. 
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Hi
I'm plan a new study that will focus on Eliomys melanurus community. I'm aware for two sample methods. the first one is to use Sherman traps and the second is to use IR camera. Do you have other ideas how to sampling population size of this extremely rare species?
Many thanks
Guy
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Because you are dealing with an extremely rare species I would recommend non-invasive sampling techniques like DNA from hair of feces. Once you have a working sampling design it will be easy to do a CMR analysis.
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I'm planning an undergraduate student field project with mark recapture on wild mice and voles, and thinking about marking methods. As individuals only need to be marked for a week I don't want to use tags. I know fur clipping is often used, but what about temporary marks with hair dye or food dye? As this is for a student project with minimal previous experience handling small mammals I'm a bit cautious about using clipping. If you have used food dye / hair dye or know of something published which did, which brand was used (or a link to the reference)?
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I used nail varnish to paint the toe nails of small mammals. I got the best results when using fast drying ones with glitter inside.
But if you want to recognise the animals after more than 3 days I would prefer fur clipping!
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The species are:
1)Muscovy duck (Goose)
(Cairina moschata) ***
2)Black Bellied Whistling Duck
(Dendrocygna autumnalis) ***
3)White faced Whistling Duck
(Dendrocygna viduata) ***
4) Fulvous Whistling Duck
(Dendrocygna bicolor ) ***
5) Snow Goose
(Chen caerulescens )
6) Comb Duck
(Sarkidiornis melanotos ) 
7) American Widgeon
(Anas americana )
8)Green-Winged Teal
(Anas crecca carolinensis)
9) Mallard Duck
(Anas platyrhynchos )
10) Northern Pintail
(Anas acuta )
11) White Cheeked Pintail Duck
(Anas bahamensis )
12)Blue Winged Teal
(Anas discors ) 
13) Southern Pochard
(Netta erythrophthalma )
14) Ring Necked Duck
(Aythya collaris )
15)Lesser Scaup
(Aythya affinis )
16) Masked Duck
(Nomonyx dominicus)
17) The Northern Shoveler
(Anas Clypeata)
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I worked many years as a zookeeper and even did some avian research on storks and ibises with several large zoos in the USA.  You really should not try to rely only on books and wildlife management academia, but ask for help from birdkeeper staff at your nearest large zoo or birdpark. Many species respond quite differently to artificial incubation, and much of the details around this is acquired only by many years of trial and error.  There are many bird curators in the AZA who could help....and some may have a great interest in promoting your research and even lending you their resources. I highly recommend the folks up at the Miami Metroparks Zoo, the Jacksonville Zoo (call Forrest Penny if he still works there) or Disney's Animal Kingdom in Orlando FL.  Disney and some other large zoos even fund researchers on joint projects involving their staff.    
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I am looking for a small mobile unit that could be used to perform DNA extraction, PCR and gel or capillary electrophoresis in the field, i.e. Not in laboratory conditions. The purpose of the kit is to perform species or individual ID. Samples would range from muscle to hair and PCR would use mtDNA or STR primers. 
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Hi Olutolani Smith
I know but not use about Palm PCR gadget
All the best,
Vladimir
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Hi, i am working with a new a rare specie of primate in Colombia named Callicebus caquetensis recently described. 
Its is located in a high fragmented area and there are estimations of poblational size which barely reach 500 viable individuals. 
I must stand a methodology for the study of its poblational density and i am not sure about the usual line transect method.
THanks in advance. 
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Dear Johana,
As mentioned by the other colleagues, all methods have their strengths and weaknesses. In my opinion, your choice should take into account the level of forest fragmentation of your study region. Highly fragmented is quite superficial. Can you tell us the number of forest fragments, their sizes and approximate shapes. Depending on their characteristics, the transect method is definitely not appropriate. Additionally, titi monkeys are "shy" primates, a characteristic that compromises our ability to sight them during transect censusing.
Good luck in your research.
Best wishes,
Júlio César
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I just want to know about any marking technique for water monitors to identify an individual from a distance.
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Whatever you do don't paint their heads! Attaching anything to the animal is going to snag, drop off or hinder growth eventually. Recognising pattern on monitor lizards is very tricky because they are often covered in dirt, shedding skin, in the shade etc. It looks easy when they are wet and freshly shed but it's not a practical way of doing it. By far the most efficient way I have found for biawaks is to cut a unique set of notches into the tail crest with a very sharp sterile blade. If it's done carefully they can be made deep enough to be permanent without hurting the animal (you can tell very easily when a biawak is hurt by its reaction). Never cut beyond the crest! These pictures show tail notches made 1-3 years previously. Mid third of the tail is best because the crest is high and they are very unlikely to lose that much tail. Sorry for late reply.
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Hello, 
I am looking for researchers which can collaborate in a paper. What I need (attached in the jpg) is plastral measurements (PL, GuL, HumL, PecL, AbdL, FemL, and AnL) of many turtles of any species, with some recaptures along time. This measurements must be taken using callipers, not measurements from photographs.
If you have them and you can be interested in the collaboration, please, contact me as soon as possible. 
Thanks! 
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Sorry Asher, but I need several measurements of the same specimens during their life. Thanks!
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Is it possible to publish a new species using only one specimen?
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Also yes, but as there may be differences depending which stage of life and as per gender, more than one specimen would be advisable.
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We are exploring potential tagging of large mammals in Namibia using small, low-cost, 'expendable' devices and we would be interested to know of experiences, publications, reports etc. that show success (so we can perhaps adapt these to the specifics of the locality)  or even failures (so we don't repeat them). In particular are there any methods which have proven effective in attaching these for periods of time without needing to capture the animal.
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I found the papers below helpful when trying to figure out how to attach a tag to horses. I particularly appreciated that the latter paper forms a reference for a low-toxicity epoxy.
Fedak, M. A., S. S. Anderson, and M. G. Curry. 1983. Attachment of a radio tag to the fur of seals. Journal of Zoology 200:298–300.
Field, I. C., R. G. Harcourt, L. Boehme, P. J. N. de Bruyn, J.-B. Charrassin, C. R. McMahon, M. N. Bester, M. A. Fedak, and M. A. Hindell. 2012. Refining instrument attachment on phocid seals. Marine Mammal Science 28:E325–E332.
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I am about to start a field season studying cinnamon teal population dynamics and we will be taking basic vegetation measurements at each nest we find.  I want to create a set of randomized points throughout the wildlife refuge in areas of different habitat, but I do not know how to determine how many points to create.  Should it be equal to the number of nests I find during each field season or should I use the same number of systematic random points each year?  Should they be in the same spots every year or should I re-randomize them in future field seasons?  It is a 14,000 acre wildlife refuge with impoundments, some of which will have water this year and some of which will not.  The teal mainly congregate in a couple of the main wet impoundments, which will therefore have very different vegetation characteristics than the dry.  Thank you for any help!
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The first thing you need to nail down is your research objective and how you will be analyzing your data then you conduct a power analysis.
See the attached paper and link. 
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We would like to observe the development of single insects on plants in the field. The insects usually settle on the bottom side of the leaf. Leaves are quite large (about palm-size) and more or less waved with some strong veins. The experiment will run about one month during summer, and therefore possible physical damage by the cages, rains and wind are additional challenges (the standard setup with metal clips and sticks can be problematic, since it is unstable and susceptible to wind especially with upper leaves which are about 30-50 cm above ground).
Now we are unsure what type of caging to use and a few ideas we had so far are:
  • Light-weight clip-cages without sticks (still fragile setup, mounting only possible at leaf edges in larger leaves bec of clips)
  • Gauze nets (covers whole leaf; prone to getting wet during rain, to heavy then or insects might drown)
  • Perforated plastic bags (too high humidity and temperatures within bag)
Do you have any better setup for such caging or another cage type or an idea how to mount a clip cage safely on such leaves in the field?
Thanks for any input.
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Any cage will modify the microenvironment about the insect. It will also influence the physiology of the leaf on a spatial scale relevant to the insect. The problems you mention for gauze nets and perforated plastic bags apply to all cages, are unavoidable, but may be worse for some strategies.
How about using a flat magnet to attach the cage to the leaf. I would make something like a clip cage, but glue the magnet to the base and use a magnet of opposite polarity on the other side (or maybe something like iron foil). It will be fairly heavy, so attach a bamboo skewer to the branch in such a way as to provide support. Might use thick wire to do the same thing.
How about using the clip cages and "gluing" them on with something like tanglefoot. I would use the bamboo skewer idea to add support. I tried to think of a non-toxic glue that would work and didn't have any ideas. Bioquip sells some nice small clip cages that may work.
In part, how well this works depends on how strong the wave is in the leaf. You could buy foam pipe, and cut it to match the wave in the leaf. Then use tanglefoot.
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Im writing a report about the Superb Lyrebird vocalisations, however am struggling to find some decent papers explaining the 'hows', and the 'whys', looking at their physical form and function, and how it facilitates their mimicking behaviour, and for what behavioural reason they do this? Any help would be greatly appreciated! Thank you
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Hannah:  Good Morning.  I have attached some papers that may give you some direct leads as to specific people to talk to directly.  One person that I would recommend is Dr. Gisela Kaplan who I am most familiar with as to her work on Australian Magpies, a species that we exhibit at my zoo.  She has done some comparative work of Magpies to other species such as Lyrebirds when it comes to vocalizations.  Hope this will move you along in your work.  Best wishes.  Thane G. Johnson, Oklahoma City Zoo
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I am investigating the possibility of setting up den cameras for my bat-eared foxes, which would allow me to record their social interactions in the den itself. These are natural dens/ hollows, and I want to do this in the least invasive way possible. Ordinary camera traps work fine for comings and goings outside the den, but I'm curious about the interior...
What equipment and set-up could you recommend?
Thanks!
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We used video-observation for nest-predation! Self-made equipment (as usual): small webcams on long flexible mounts (goosneck flexarms, e.g. manfrotto). Videoobservation is much better than cam-traps, you have no delay!
The collar-cams for cats are quite cool. The best seem to be those of National Geographic. However, you may not buy, but only rent them - for a fee of 300,-€/week.
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A camera trap data study was developed, installing cameras for 21 days, but we completed all camera station points in a long period (24 months). Individuals of target species were identified.
This long period may include the inclusion or elimination of individuals of the study area, violating the assumption of closed population for capture-recapture methodology. There is another methodology to estimate abundance and density?
Thanks!
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Clearly, you can't use closed CR models for the entire 24 months. The problem with using Jolly-Seber-type open models (for example with monthly sampling occasions) is that the population may not be open enough from one month to the next, so your estimates of phi (apparent survival) will be close to the boundary of 1 (and unreliable).
The other option is to use a robust design approach, either spatial (e.g. the Gardner et al. paper mentioned above) or non-spatial. However, to use the robust design, you will have to chop a lot of data so that a) you can define very short closed periods during which births/deaths (and in the non-spatial models, even movement) is unlikely, which are b) separated by long periods (during which data are discarded) when the population is open to gains and losses. While the spatial CR models are certainly better, the open model SCR versions have serious computational issues that may make them infeasible.
The other class of models for unmarked animals (e.g. Royle & Nichols 2003, Chandler & Royle partially marked, Royle N-mixture, etc.) mentioned above all require that you are repeatedly sampling the same population multiple times, to allow you to separate non-detection/capture from absence.
Finally, the closure assumtion does not state that gains (from births/immigration)=losses(from deaths/emigration), it states that there are NO gains or losses.
Hope this helps!
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I have more than 300 genotypes and I want to measure CC in the field on these genotypes which are many. I can I do this in two subsequent days.
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Chlorophyll content mg/g has to be calculated in spectrophotometer. 652 nm for total chlorophyll,645nm for chlorophyll A and 663 for chlorophyll B.And the 300 samples are easy to do in one day.Pluck the leaves take the wight and put it to 80% ACETONE solvent,keep in dark with room temperature. Extract and finish the whole work by 2-3 days.
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I am working on several projects with scorpions and Madagascar hissing cockroaches. If the camera also worked for shooting into a fish tank, that would be great too (as I also work on electric fish, and I have had issues in the past with the IR light source on Sony Handycams reflecting back off the glass of fish tanks.)
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Hmmmm, I got this from GoPro:
Hi Sara,
Unfortunately the HERO cameras do not have that capability they also can not shoot very well in very dark conditions. Please let me know if you have any other questions.
Many Thanks,
Cody A.
GoPro Support
ref:_00Do0HJuF._500o02lWyU:ref
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We are trying to estimate the occupancy of snow leopards in Rolwaling valley, Nepal. How much area should we cover for this study? Do we need to cover atleast area equivalent to approximate home range or should we take more than that, or can we take less than that?
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Dear Jeevan:
The sampling unit should be slightly higher than the home range for the target species to avoid spatial correlation. The goal is evaluate occupancy (ψ) and detection probabilities (p) for population in the landscape, and you'll need a number high enough of sampling unit and several temporal replica to evaluate them.
See the attached paper from MACKENZIE & ROYLE
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I need to catch some Asian Openbill Storks to track their movement. Does anyone know how to catch them. This birds like feeding in shallow water areas and roosting on trees.
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Maybe you can contact Libor Peske - expert on wildlife tracking over the world - which tracking black storks, eagles, ibis and other species. here is a contact to him - lpeske@volny.cz...He is known for the ability to trap rare species in wildlife.
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Color-banding related question: I'm studying Hispaniolan Woodpeckers in mid-elevation (~550-700 m) tropical, fairly open habitat, and I have had some issues with Darvic color bands (specifically, a large number of my Darvic bands inexplicably opened by themselves in my banding kit- a plastic tackle box). I'm considering incorporating Acetal color-bands (http://www.avinet.com/avi_order.taf?_function=view&ct_id=101) to supplement the striped celluloid bands I'm already using.
Has anyone run into major issues using Acetal bands in tropical climates? Do they have to be sealed shut? Is there a method other than application of heat that can be used to seal the bands? 
Thanks!
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I've had darvic bands open up because they were subjected to really hot temperatures in a car (left on a dashboard or on a seat). Usually they are ok in a banding kit away from the sun, but it can get pretty hot in a closed up car. Keep bands out of direct sun and hot temps and you should be fine. 
I'm not sure if I used acetal colors with the birds I banded in the tropics, but I use them in my current project in temperate climates. They're just like darvic bands. I only seal depending on the bird species. Cardinals and blackbirds will take a band off so they get sealed. Chickadees, warblers etc. don't usually bother with trying so I don't seal and just press shut. If you need to make cut the band smaller (which with a woodpecker I imagine you don't), I would definitely seal. I used a high temp cautery loop tip to seal this summer and it worked great, but I broke it quickly. I imagine you could use super glue too (with caution to not attach to the bird's leg, I don't particularly like doing this), but I don't believe it will melt with acetone like other material. 
Hope this helps. 
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I am looking for a GPS unit helpful in field biology. A handheld unit, affordable and easy to carry.
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I usually work with Garmin 60Csx and 62Csx, like Galo. But now there is a new option Garmin GPSmap 64st . All of them are relativily cheap, weight is ok, and the new one has a very good improved signal (GPS+GLONASS). 
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I recently work on the diet analyses for woodland migrants. I found couple of spring-like and brown or pinkish structures from bird fecal samples. It feels like rock or iron when I try to break it. Does anybody know what they are? Thanks in advance!
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They resemble some sort of pupae a little like #3. Cant really see the ends in the photo. Were you able to break them?
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I estimated survival in Mark. All survival probabilities was estimated per month. To get annual survival I just raise into power of 12 (12 month). but how to obtain SE for this annual rates? Probably not by the same way, as SE for annual survival should be greater then for monthly rates, I suppose.
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You can find your answer here: Powell, L. A. (2007). Approximating variance of demographic parameters using the delta method: a reference for avian biologists. The Condor, 109(4), 949-954.
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Field conditions may scientifically never be truly standardized because of perception constraints, logistic constraints or continuous dynamics in nature. The need to standardize experimental environments may depend on the scientific problems addressed or model systems considered. As an example, between-population variation in timing of reproduction in blue tits (a small European nest-box breeding bird) is sometimes larger in scientifically more standardized aviary conditions than in scientifically less standardized free-ranging conditions. Responses of blue tits to ‘artificial’ versus ‘semi-artificial’ conditions may result from scientifically ‘uncontrolled’ organism-environment interactions. Not all study populations may be preadapted to captivity and scientists most often don’t know this when they initiate laboratory experiments. Veterinarians may advise to use sterilized test cages minimizing infection. The practical problem is that blue tits will not breed in these highly artificial environments or that some populations cope better with captivity than other populations. Outdoor aviaries with ‘semi-controlled’ natural vegetation might be more appropriate for captive wildlife breeders, simply because they better simulate wildlife conditions. How can a veterinarian or members of ethical commissions that never worked with blue tits provide constructive advice about both scientifically and ethically acceptable experiments? Should ‘environmental sterility’ or the ‘mental state of captives’ been used to make decisions about how to conduct experiments? Do sanitary recommendations proposed by people not familiar with model species complicate execution of scientifically acceptable experiments that take background knowledge from model species into account? Sanitary conditions are never truly controlled in wildlife conditions anyway.
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I think an intimate knowledge of the ecology, (and, if relevant, of the social behaviour) of any organism would be a prerequisite for an ethical decision about it, be it bird, grasshopper, or starfish. All  a veterinarian could offer would be an opinion on likely pathologies. Make sure you have a competent zoologist on your ethics committee. 
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Currently, my colleagues and I are in the first stage of preparing a article about gender determination of Long-eared Owls (Asio otus) based on plumage coloration and biometric measurements supported of DNA analyzes. For now, we found several close related papers which we have been able to found on the Internet databases (Scopus etc). Thank you in advance for your help. 
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Entries in my database on Identification and Long-eared Owl:
Baker, K. (1983): Guide to ageing and sexing non-passeriformes (part. 7). Ringer's Bulletin 6: 45.
Baker, K. (1993): Identification guide to European non-passerines. British Trust for Ornithology, Norfolk.
Gálvez, R. A., L. Gavashelishvili & Z. Javakhishvili (2005): Raptors and owls of Georgia. Georgian Centre for the Conservation of Wildlife and Buneba Print Publishing, Tbilisi.
Martínez Climent, J. A., Í. Zuberogoitia Arroyo & R. A. Moreno (2002): Rapaces Nocturnas. Guía para la determinación de la edad y el sexo en las Estrigiformes ibéricas. Monticola, Madrid.
Mikkola, H. & J. Lamminmäki (2014): Moult, Aging and Sexing of Finnish Owls.
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As part of my MSc project I am planning on collecting hair from wild foxes (Vulpes vulpes), but I am trying to avoid using barbed wire for ethical reasons.
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I've collected wild dog/dingo hairs or epithelial cells for DNA analysis using two methods. One using a food lure placed on very fine (~600 grit) sandpaper, stapled to a 100 x 100 x 10mm piece of timber. A second very successful method was using a canid lure (Magna Glan and Canine Call worked for us) that elicited a rolling response. We placed a drop of this lure on a 1cm cube of sponge rubber on a sticky surface. Adhesive tape wrapped around a timber block (dimentions above) with sticky side out, sponge rubber/lure in the middle. Place these at scent stations or travel ways where foxes are likey to encounter them.
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Hi Everybody
We are developing a framework for monitoring free roaming dog populations in the cities of Tierra del Fuego. The objective is to monitor the mid and long term success of the policies to reduce free roaming dogs in the streets of the cities, like neuter and responsible pet ownership. Cities are expanding in surface and adding new neigborhoods over the course of the years.
For that reason, and to avoid restrictions of design-based surveys, we are considering the use of Density Surface Models, also to be able to explain changes in dog presence by covariates.
Then, we should be able to tell the towns to follow a series of tracks (streets) that need to be surveyed over the years. Adding covariates, we should be able to develop a DSM to assess abundance based on these covariates.
Then, here comest the two questions:
ONE: The issue that comes to my mind and I want to share with you hast to do with modelling all over the space of the city, when free roaming dogs are distributed only along the streets. The, the streets are like a mesh of something like 21m wide, separated by the about 800 blocks of around 90m side.
Potential solutions I was thinkg were:
1. Model the data as if they were collected and build a prediction grid where blocks can´t hold dogs (as if they are "0") meanwhile streets has a value of "1". Then I wonder how much the smoothing all over the surface will affect the predicted results.
2. Model the data, but adding "dummy" transects located over some of the blocks, just to tell the model that inside the blocks there are no dogs... However the modelling may be affected by the spatial spread of these dummy transects.....
3. Use something like the soap film smoother but I can´t figure out how we can handle such amount of blocks...
TWO:
About detectability of dogs. When travelling along the streets we need to record dogs that can walk freely at the sidewalks or at the streets. Streets has parked cars along the sidewalks, and many houses do not have fence, so dogs can sleep inside a parcel but leave the parcel boundarie as soon as they want to bark or whatever. This impose visibility issues that affect detectability.
To reduce that I was thinking in make dogs more visible:
1. Survey the streets going behind garbage collectors, as these guys atract dogs either by their behavior (running along the streets) or leaving garbage behind ocasionally).
2. Broadcasting dog barks from the car meanwhile we go travelling. I know that this affect the results of a survey, but if we want to see dogs in the streets I understand that we need to make them out.
Any idea or previous experience in that is welcome. Many thanks
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Hi,
As an exercise as part of a population estimation course, students at a population estimation course I taught applied closed capture recapture sampling and modelling to estimate stray dog numbers in an urban area in south India. It worked pretty well back then, and now there are advances in spatial capture recapture which will allow you to define dog habitat and non-habitat (1/0), explore fine-scale spatial variation in density, account for movement of individuals within and even out of the sampled area, among many other benefits.
This would work best with photography using hand-held cameras across the area of interest rather than fixed location camera traps. However, this brings up the issue of how you would analyse the data: you could use the SCR models developed for area searches, but for which coding would have to be done in BUGS/R. Or you could use mid-points of your search segments (as long as you keep them short) as approximations to fixed location camera traps (or other passive detectors) and use software such as SPACECAP (see link below) or DENSITY to analyse your data easily.
All the best!
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Asociacion Armonia is protecting a 11,000 acre tropical savanna in the Beni, Bolivia. We are going to use a savanna patch-burn management technique, but we are not clear of the potential climax level of older successional savannas. We are thinking the best measurement could be arthropod diversity and abundance. We are interested in an comparison arthropod studies in tropical savannas.
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Probably some of these: 
Frizzo, Tiago L. M. ; Campos, Ricardo I. ; Vasconcelos, Heraldo L. . Contrasting Effects of Fire on Arboreal and Ground-Dwelling Ant Communities of a Neotropical Savanna. Biotropica (Lawrence, KS), v. 44, p. 254-261, 2012.
FERREIRA, R.N.C ; Franklin, E. ; Souza, J. L. P; Moraes, J.. Soil oribatid mite (Acari: Oribatida) diversity and composition in semi-deciduous forest fragments in eastern Amazonia and comparison with the surrounding savanna matrix. Journal of Natural History, v. 46, p. 2131-2144, 2012.
SILVA, LAURA V. B. ; Vasconcelos, Heraldo L. . Plant palatability to leaf-cutter ants (Atta laevigata) and litter decomposability in a Neotropical woodland savanna. Austral Ecology (Print), v. 36, p. 504-510, 2011.
Lopes, Cauê T. ; Vasconcelos, Heraldo L. . Fire Increases Insect Herbivory in a Neotropical Savanna. Biotropica (Lawrence, KS), v. 43, p. 612-618, 2011.
AMPOS, Ricardo Ildefonso de ; VASCONCELOS, H. L. ; ANDERSEN, A. ; Frizzo, Tiago L. M. ; SPENA, KELLY C. . Multi-scale ant diversity in savanna woodlands: an intercontinental comparison. Austral Ecology (Print), v. 36, p. 983-992, 2011.
SANTOS, E. M. R. ; FRANKLIN, E. ; MAGNUSSON, W. . Cost-efficiency of Sub-sampling Protocols to Evaluate Oribatid Mites Communities in an Amazonian Savanna. Biotropica (Lawrence, KS), v. 40(6), p. 728-735, 2008.
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I'll be observing grey reef sharks (3) within an aquarium and trying to find a way to randomly allocate time slots for each shark for a focal sample. Observations will take place over several months for 2/3 days per week. Each observation day is then split into 3 time periods AM, NOON, PM (1 slot for each shark). This leads me onto...
Is there a method which takes all the observation days into consideration so that at the end- each shark would equally cover ever day of the week and all three time periods for each day?
Thanks for reading, I hope I've explained it ok?
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You have a latin square with 3 times of day and 3 shark tanks!! Check any stats book on the matter, and make sure to keep that desing structure in your analyses.
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Dear Colleagues
What is the sex ratio in carabids?
As you all know pitfall trapping gives a bias estimate of abundance due to various reasons. Therefore higher abundance of males or females in the trap does not have to relate to their abundance. Do you know sex ratio of ground beetle populations obtained with more reliable methods than Barbet traps? Do you have some unpublished data on this topic?
With kind regards
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Hi Marcin
We did some hand sampling in alluvial areas of Aare and Bünz. At each site we have cought Carabids in fourty parcels three time periods spring, summer, late summer, 20 minutes per parcel and time period.  See below the pooled species and the sex ratios. I will not test it yet but I guess the results endorse your 1:1 sex ratio for most species and the total too.
 
 
 
Art (lateinisch)
Male
Female
Acupalpus meridianus
1
2
Agonum micans 
6
8
Agonum muelleri 
12
19
Agonum sexpunctatum 
 
1
Agonum viduum 
2
4
Amara aenea 
12
15
Amara familiaris
 
1
Amara ovata 
5
5
Amara schimperi 
4
2
Amara similata 
3
1
Anchomenus dorsalis 
4
6
Anisodactylus signatus
3
1
Anisodactylus signatus 
4
3
Asaphidion pallipes
1
1
Badister lacertosus
 
1
Bembidion articulatum 
 
2
Bembidion ascendens 
7
20
Bembidion atrocaeruleum 
78
63
Bembidion decoratum 
1
1
Bembidion decorum 
52
46
Bembidion fasciolatum 
14
21
Bembidion femoratum 
46
44
Bembidion genei illigeri 
1
 
Bembidion lampros
3
2
Bembidion milleri 
 
1
Bembidion prasinum 
12
6
Bembidion properans  
9
5
Bembidion pseudascendens 
9
12
Bembidion punctulatum 
22
19
Bembidion pygmaeum 
1
 
Bembidion quadrimaculatum 
1
1
Bembidion schueppeli 
1
 
Bembidion semipunctatum 
1
2
Bembidion testaceum 
31
25
Bembidion tetracolum 
47
63
Bembidion tibiale 
1
 
Bembidion varicolor 
5
3
Brachinus explodens 
3
 
Bradycellus verbasci
 
1
Carabus granulatus 
 
1
Chlaenius tibialis 
8
7
Chlaenius vestitus 
4
5
Clivina collaris 
9
5
Clivina fossor 
2
2
Demetrias monostigma 
1
 
Diachromus germanus 
9
10
Elaphrus aureus
 
3
Harpalus affinis 
35
24
Harpalus distinguendus 
14
8
Harpalus luteicornis
 
1
Harpalus progrediens
1
 
Harpalus rubripes    
3
3
Harpalus rufipes 
4
8
Harpalus signaticornis 
1
1
Lionychus quadrillum 
41
42
Loricera pilicornis
4
2
Nebria brevicollis 
2
6
Nebria picicornis 
1
5
Notiophilus palustris
1
1
Oodes helopioides
 
1
Ophonus ardosiacus
3
2
Ophonus azureus 
9
6
Ophonus puncticeps
2
 
Oxypselaphus obscurus
1
 
Panagaeus cruxmajor 
2
2
Paranchus albipes 
30
25
Parophonus maculicornis
1
 
Patrobus atrorufus 
2
2
Platynus assimilis 
4
3
Poecilus cupreus 
8
13
Pterostichus anthracinus 
1
1
Pterostichus melanarius
1
1
Pterostichus nigrita
 
1
Pterostichus vernalis 
 
1
Stenolophus teutonus
8
8
T. parvula
4
4
Tachys bistriatus 
1
 
Tachys micros 
4
4
Tachyura quadrisignata 
59
67
Tachyura sexstriata
3
3
Thalassophilus longicornis
1
 
Trechus obtusus 
1
2
Trechus quadristriatus 
2
2
Trechus secalis 
1
2
Total
690
691
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We are having data on Bluethroats from its breeding and wintering grounds and would like to study their spatio-temporal migratory connectivity.
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In addition to the the PLoS ONE paper above, see also
Ruegg, Kristen, Eric C. Anderson, Kristina L. Paxton, Vanessa Apkenas, Sirena Lao, Rodney B. Siegel, David F. DeSante, Frank Moore, and Thomas B. Smith. "Mapping migration in a songbird using high‐resolution genetic markers." Molecular ecology (2014).  http://onlinelibrary.wiley.com/doi/10.1111/mec.12977/abstract
and
Rundel, Colin W., Michael B. Wunder, Allison H. Alvarado, Kristen C. Ruegg, Ryan Harrigan, Andrew Schuh, Jeffrey F. Kelly et al. "Novel statistical methods for integrating genetic and stable isotope data to infer individual‐level migratory connectivity." Molecular ecology 22, no. 16 (2013): 4163-4176.
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Forest Type: Dry Deciduous Forest.
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This is Bridelia retusa, a tree species in the family Euphorbiaceae
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I am involved in analysing a capture-mark-recapture survey dataset that covers in excess of 30 years.  I am trying to establish whether this is in fact the longest running survey of its type in existence. I have yet to find another survey that has been running continuously for such a long period of time. I though this would be the place to ask! 
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Soay sheep of St.Kilda (30yrs): Clutton-Brock, Pemberton, Coulson, et al.
Red deer of Rum (44yrs): Clutton-Brock, Coulson etc
African Lion (~50 yrs). Craig Packer
Olive Baboon (>40). Craig Packer
Florida Scrub Jay (>40): John Fitzpatrick, Reed Bowman
Red Cockaded Woodpecker (>30): Jeff Walters
Great Tits of Wytham woods (>60): Ben Sheldon
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For example, if a dead tissue (e.g. metazoan) was left in an actively fermenting medium (e.g. beer), how would this affect the quality of the DNA one could extract or amplify from this tissue?
Personal experiences or papers about this?
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Since you are hiding many things in your question; it is rather difficult to answer you precisely. For example: What was the fermentation all about? What is the biological specimen you are referring to? Let me tell you that in a routine fermentation, with bacteria or fungi normally it should not affect. However, it is well known to all fermentation technologists that how so ever, one is claiming the culture to be pure, it is often contaminated with a virus. Secondly, during the several life cycles of the microbe, several things will happen like simple conjugation or transduction and then, the picture will change (of course, ultimately the frequency of these phenomena is important too). lastly if not the least, the stress that the organism underwent (if any) during any stage of its growth. Like these there are several other phenomena that could take place during a fermentation process which may or may not affect the quality of DNA.  
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Long-tailed macaques are primarily arboreal (and are quite elusive in our site). Tracking them in the wild to observe defecation events requires A LOT of input. I'm fully aware of the huge difference between captive and wild populations but would it still be acceptable to do so?
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Before you go any further, I guess you should clarify what your aims are. Do you simply want to track the over-time variation in population size, or get reliable estimate of population size? In the first case, you may consider to use simpler population indexes (faecal group count -FGC- can be really time-consuming!). If population abundance is what you need, then FGC might be an option, but:
- as Kimberly said, its use largely depends upon the reliability of defecation rate (you should provide more details about your captive population: how about the size and environmental features of the enclosure, are they in any way comparable to the wild? Are captive animal fed ad libitum or not? Does defecation rate vary according to season?...). If you think the captive population live in conditions somewhat comparable to the wild one, then you may -with some caution- use that defecation rate (lots of studies simply assumed defecation rates based on other studies, sometimes on different species!);
- even if you can obtain reliable estimates of defecation rate, FGC may be affected by several other sampling issues, so pay attention to your sampling protocol! (normally you need a lot of plots to get reliable estimates, and this can make fieldwork really really tedious! A good sampling strategies, for example, could be to divide you area in grids and pick a random plot within each grid -is your area fully accessible? Otherwise you may risk to bias your estimate. Plus, are you 100% sure you can find all scats in the field? I am not a primatologist, but you talked about elusive species in a forest environment...that sounds tricky =)
To sum up, FGC is mathematically sound, but there are a lot of practical sampling issues to take into account. As said before, if you simply want to track the over-time variation, I would definitely not bother using FGC. If your aim is to obtain estimates of population size, you may use it, though I wonder if have the chance to try other strategies (mark-resight? camera traps? distance sampling? They also have flaws to be aware of, but at least the fieldwork required is much less than FGC.
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This may be an odd question for ResearchGate, but although I can find much in the way of products I can find little in the way of reviews and opinions. I am looking for a good, reliable, accurate hygrometer and thermometer (combo?) to use in the field (Spanish countryside) to record the humidity and air temperature at night. Any recommendations or advice on models? We don't want to go too cheap and risk bad data but we also do not need top of the line as it is supplementary information. Anyone have any experience?
Thank you in advance.
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Hello,
I currently maintain a network of stations with different kinds of probes:
- Vaisala HMP45 (old ones) and HMP155: these are excellent sensors, with a very low deviation in time, but expensive;
- Rotronic HC2 series probes : (much) less expensive and of high quality. I compared these ones with both Vaisala probes and with the temperature from a PT100 (wired with wheatstone bridge, with high quality resistors) and found it extremely accurate (< 0.05 °C difference with the PT100, which is beyond product specifications). Anyway you can expect a resolution <0.1°C and 1% humidity, which is suitable for common applications.
We're about to test very cheap probes that come with raspberry pi. I have no clue about the quality, but I'm a bit dubious regarding the conditioning (these electronics are not all-weather proof).
Another aspect that might be of importance in your choice is the interface you use to collect the data. I'm using Campbell Sci. dataloggers for analogic to numeric conversion, pre-processing and storage. If you want a numeric signal right out of the probe I guess it may become much more expensive.
Hope this help, I can give you more detailed probe references if needed.
Best,
Jerome
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I am getting ready for this summer's field season and looking to buy a good sturdy GPS unit with reasonable accuracy including elevation. Any recommendations?
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I wish the 60 Csx was still available, it hasn't been made for years now. In the coastal plain none of the cheap units have good elevation. But if +/-40 ft is ok then there you go. If you get a unit that is map capable they have units that can have topographic maps loaded to them. Where I am the topo maps are more accurate in elevation than the GPS because +/- 40 feet here is the difference between the elevation of most of the state. If you have to operate in mountains or under dense canopy you will have poor accuracy without a quadhelix antenna like on the Garmin 62 or 64 although I am not endorsing those. Often in high interference areas the $1000+ units although more accurate on open ground, have algorithms that have difficulties with satellite signals that are distorted or bounced by vegetation or buildings or mountains.
Garmin at one time had a great program called MapSource for dealing with maps and tracks, and lots of waypoints. In the last few years they discontinued that for a dumbed down version that is a pain to use for scientists with hundreds of waypoints. I guess they are aiming their software toward tourists who just don't have the waypoint management issues that field scientists have.
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