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Herbivory - Science topic

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I'm looking for papers/research on insect floral & seed herbivory on alpine thistles. However, I'm having trouble finding any information. Do you have or know of any papers that quantify the loss of flowers and seeds to inflorescence-feeding insects on HIGH MOUNTAIN (alpine) thistle species (especially CIRSIUM, CARDUUS)? Or any papers on this topic on ANY Asteraceae of the high alpine mountains?
I would appreciate ANY help you can give me - reprints I've missed (pdf), or references I should seek, or any clues to who might be doing this type of work.
THANK YOU! Svata Louda
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This is my question, so I do not have an answer!
I am still looking for information on the interaction between insects and alpine plants, especially alpine thistles (Cirsium spp). Any help or clues will be appreicated!
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Suppose there is a population of herbivorous species undergoing the rewilding phase. Following this stage, what steps should be taken to.
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Integrating a rewilded population with the main population during release involves careful planning to ensure ecological, social, and genetic compatibility. Here are some strategies to achieve successful integration:
  • Pre-Release Assessments: Ensure ecological suitability, genetic compatibility, and health safety of both populations.
  • Behavioral Conditioning: Train rewilded individuals for natural behaviors and social integration.
  • Soft Release: Gradual adjustment via transitional habitats and initial resource support.
  • Staggered Release: Phased introduction to reduce ecosystem strain and allow monitoring.
  • Social Integration: Use main population members as mentors and address conflicts.
  • Environmental Enrichment: Provide diverse resources to minimize competition.
  • Post-Release Monitoring: Track health, behavior, and interactions with adaptive management.
  • Community Involvement: Engage locals for support and habitat management.
  • Ecological Corridors: Ensure habitat connectivity to promote natural dispersal.
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I'm interested in the earliest days of placental terrestrial locomotion in large herbivorous taxa. Phenacodus seems to be transitional in this regard. Any others?
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Patrice Showers Corneli I had to look up your term, "tree-dwelling Perissodactyls" since I knew of only terrestrial perissodactyls. I came up with one: tree-dwelling hyrax. Can you name a few "tree-dwelling Perissodactyls" by genus? Perhaps list only those known from more or less complete skeletons. No dental taxa, please.
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Throughout the literature, it is unclear whether algal turfs (i.e. dense assemblages of short, turf-forming algae) are a form of algae that occurs due to the effects of disturbance (waves, herbivory) or if they represent a morphological advantage that has evolved over time.
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In intertidal habitats, algal turfs surely are advantageous as, while exposed during low tide, they help keep the moist and provide shade, thus protecting from desiccation and UV-stress. This is particularly helpful for younger fronds, germlings and sporelings, who still lack the chemical molecules that help overcome those stresses. They have the same beneficial effect for benthic infauna. And they shelter the infauna from bird foraging by making harder for birds to scout inside the denser turfs. Likewise, underwater, denser turfs make harder for herbivores to scout and forage on the juveniles and germlings. Check some of my literature and references their in. Best Wishes
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With or without upwelling the copepoda Paracalanus quasimodo is present in high abundance in Cabo Frio. What would happen if this species was lost in the region, would the second most abundant species (Temora turbinata) take its place? Both preferentially herbivorous and highly related to the phytoplankton peaks present all year round.
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It's a possibility, since they both coexist but Paracalanus quasimodo seems to have a regulating role in the occurence of Temora turbinata (probably because the first one is a better competitor or there are a super little difference in their niches that favors the most abundant species, among other factors), however it will depend also in the absence of changes in Temora turbinata niche, mainly regarding predation interactions and resources... Assuming there won't be a natural predator for Temora turbinata (in case of the lost of Paracalanus quasimodo) and no changes in its resource amount, for exemple, this species may be expected to become the most abundant one. Despite that, I think that a (natural) factor strong enough to cause the lost of Paracalanus quasimodo may also cause the lost of Temora turbinata, since they're so alike :)
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Tropical grassy biomes, such as savannas, are often described as disturbance driven because of the important functions of consumers, namely fire and herbivory. When does a consumer shift from being a consumer to being a disturbance?
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Hello Peter; I'd guess that when the species distribution of the producers starts to change, the consumers have begun to unsettle the producers and so create a disturbance. Assigning a causal relationship would be the tough part since weather and climate variability also play their parts. Best regards, Jim Des Lauriers
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I'm looking for a protocol to apply simulated herbivory treatment on plants by spraying methyl jasmonate or jasmonic acid. If anyone has a detailed lab protocol to share that would be much appreciated!
I am also wondering, what is the difference between using MeJa or JA for the treatment? Is there any difference in terms of the expected response from the plant?
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Hello Kristiina; You might find some useful information in this paper.
Thaler, J. Jasmonate-inducible plant defences cause increased parasitism of herbivores. Nature 399, 686–688 (1999). https://doi.org/10.1038/21420
Best regards, Jim Des Lauriers
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We will investigate the relationships between large herbivore movement and biodiversity. For this we need to track Oryx, Eland and Greater Kudu's. I am in contact with some companies (Lotek (UK), GPScollars (UK), African Wildlife Tracking(RSA), Vectronic (GER), Followit (SE)), but still would like to know if you have any recommendations for GPS collars for large herbivores in Southern Africa with irregular GSM-Network.
Thank you very much for sharing your expertise.
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Hi Robert! Great to hear that you are happy with the Vectronic collars. As you are getting acceleromtry you should have a look at https://www.schaeuffelhut-berger.de/wordpress/en/services/products/products-firetail-eng/ It is simply fantastic at getting to actullay see the accelerometer data in connection with the locations. It works best via Movebank.org and you will need to get a special script from them to convert the acc data from the output from Vectronic's own Motion Data Monitor. Let me know if you need further advice.
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Equines as domestic herbivores and pack and riding animals face a serious challenge due to the expansion of rural road and motorized transport. What has to be done to keep their legacy in the smallholder farming systems?
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Hello Takele; What an interesting idea! I have the good fortune of living in an affluent society (Southern California). There are horses in many neighborhoods. The horses are pets, not workers. In nearby, rural areas, that pet status is also true...and includes a nostalgia for the "good old days".
I think that it is true that the livestock is nostalgic if farm work can be mechanized economically. Horses, mules and donkeys eat a lot and require more attention and expense than a tractor does. So the farmer compares the ongoing costs and benefits and decides.
Subsistence farmers use equines out of simple necessity. Making a serious effort to talk to such farmers about their economic judgements might reveal some way to approach your question. Would a person with a battered old tractor return to using horses? Why?
Best regards, Jim Des Lauriers
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Hi there! I am interested in understanding (or making myself more confused, whatever) the evolutionary pathways of coprophilic habit in dung-inhabiting fungi. Taking into account the dung of herbivore animals as a substrate to dung fungi growth, we have few "candidates" to be dung-producers with some requirements to early dung fungi (e.g. the amphibians Ichthyostega (I don't know if it was an herbivore or omnivorous, appearing about ca. 375 million y/a in Devonian, once the first tetrapod herbivores made their first appearance in the fossil record near the Permio-Carboniferous boundary, ca. 300 million y/a.). Terrestrial plants made their first appearance ca. 450 million y/a, with a well-accepted role of arbuscular mycorrhizal fungi in this process. So, my question is about if there is some study dealing with the evolutive process of dung-inhabiting fungi, presenting some consideration where and how, in the evolutive process, this ecologic habit firstly appears? Any considerations are welcome! Thank you!
If you want to help me with this question with more details (or more questions ¯\_(ツ)_/¯ ) or papers/books, feel free to also send me an email at: calacafjs@gmail.com.
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Also kindly check the following very good link:
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As insects become more resistant to pesticides, the “smell of fear” some predators produce may someday be harnessed to repel and disrupt destructive insects naturally. In a recent study, a team of researchers found that the synthesized scent of a ladybug had measurable effects on their natural prey aphids in the lab, and the next step will be field tests. Plant-eating bugs pose threats to farmers and gardeners, prompting the use of pesticides. In the study led by Hermann, predator insects emit odors that their herbivorous prey can detect. This, in turn, changes pests’ behavior and even their physiology to avoid being eaten. The researchers have found a way to capture the “smell of fear” to obviate the need for harsh chemicals.
Farmers are known to use massive amounts of pesticides to get rid of the hordes of hungry insects that are destroying their crops because herbivores are a major threat to crop yields. These pesticides often cause massive environmental problems. They can reach our food, harm humans, threaten bees, kill birds, and destroy populations of predatory insects as well, making the crop pest problem worse in the long run. So one alternative that researchers and farmers have been testing is to use predatory insects to control plant-eaters. However, this approach - known as biological control - has its own challenges, as the release of many natural predators may not always target the intended species, in addition to the fact that some pests are invasive and have no native predators, and may even prey on each other in the end.
So, what is your scientific opinion on harnessing the natural smell of predators as a promising future direction of chemical ecology applied in sustainable pest control?
All comments and contributions are welcome.
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The predators are also very reliant on environmental conditions – temperature and day length can alter their behavior so they may only be effective during certain seasons. This, along with the fact that some pests are invasive and have no native predators means some pesticides may still need to be used, which can then also impact the predators.
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Hi everyone,
I have 8 water quality parameters to explain the herbivory rate of sea urchins in seven different sites (80 observations in total). I have done a multiple linear regression and results showed that several parameters are significant drivers for herbivory rate.
I have also done an RDA on sea urchin abundance vs water quality (both multivariate) and visualized it, but somehow I am confused on how to visualize the herbivory (univariate) vs water quality. Is it still possible to do an RDA on this type of data? I understand I can make a residual plot of the regression, but I'm wondering if I could still have ordination arrows on the plot for herbivory vs water quality.
Many thanks, hope the description is clear enough to understand. I appreciate any feedback and suggestions.
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Before you do the RDA, you should check the length of the extracted gradients using a DCA, then decide whether you should perform A CCA of RDA. For MLR, I think you have few observations (8 sites) for the many water variables you mention. You instead consider the more flexible PLS (Partial least squares projection to latent structures) MLR to avoid overfitting your data.
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I have camera trap data with its surrounding habitat quantification data.
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Thank you Andrew sir for valuable suggestion.
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I have above ground biomass values of fodder species of the certain area.
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The " "k" - carrying capacity" is the theoretical equilibrium population size at which a particular population in a particular environment will stabilize when its supply of resources remains constant. You also need to know about your forest production capacity, as well these herbivores maximul intake capacity.
You will find more answers in these three publications :
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It occurs to me that nursery-grown plants (in the absence of herbivores) do not develop (inducible) defenses, and that when planted out, may suffer greater herbivore damage, at least initially. Does anyone have examples of this, or suggestions of it, from the literature?
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Another aspect you might want to consider is that inbreeding in plants can increase herbivory susceptibility (e.g. Kariyat et al 2013, American Journal of Botany, 100(6), 1014-1021). As nurseries generally provide benign conditions, inbred offspring survive which would die under more harsh natural conditions (e.g. Ismail et al. 2014, Conservation Genetics, 15(3), 533-545). This might be another reason why nursery grown seedlings appear more susceptible to herbivory. Just an idea I have been thinking about.
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Suppose, I want to study a grassland. I want to know what population size of herbivore of same or different species can sustain easily? What are the methodologies? What kind of precaution should be taken for this type of research? Is is possible to measure it's carrying capacity? Suggest me please. Thanks!
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Carrying capacity can be estimated by calculating total area and total no. Of population of that area.
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Need advice on feasibility and pitfalls associated with parasitological (molecular or traditional) testing of old fecal samples from animals (herbivores and carnivores). the samples range from 1-15 years in age. some preserved in refrigeration but most kept at RT in dry (hopefully) boxes.
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Dear Bindu Raghavan , I used only traditional morphological (sedimentation, flotation ovoscopy + larvascopy) methods. But if there are live parasites I see no reasons preventing molecular research.
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I need to perform some assays of the relationship between the leaf area loss and the age of the leaf, but I have no experience with these. Do you have any idea?
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Hi,
I've a big problem with analysing some field data of my master thesis. I recorded herbivory damage on plants in a transplant experiment along an elevational gradient with 30 different Brassicaceae species.
So I have 5 different sites at 5 elevations (600, 1000, 1400, 1600 and 2000 m). In each site, there are 30 different plant species with different elevational distribution (10 low-elevation, 10 mid-elevation, 10 high-elevation plant species), with 20 individuals per plant species = 600 individual plants at each site.
Each week from August 2018 until August 2019 I scored the herbivory damage on the leaves of all the plants with a scale from 0 to 5 (0= no damage, 1 = small feeding marks, 2 = <25% damaged, 3 = >25% damaged, 4 = >75% damaged, 5= completely eaten.
Now I'm trying to analyse my data but it is quite difficult.
I have these variables:
- taxa = plant species,
- elevation class = mid/low/high elevation class (or origin),
- site = 600/1000/1400/1600/2000
- damage score = values from 0 to 5 (ordinal variable)
- date of measure (date at which the damage was scored).
I add a printscreen of how data look like.
My main problem is that between all the variables, the number of observations changes, because some plants died or did not germinate (= different n obs between taxa, site and elevational class) or some sites could not been checked because of snow on the site (= different n obs between sites).
I would like to know if there is a way in R to standardize the number of observations across variables and across time.
I tried with the sample function and it works if I sample by site, taxa and elevational class. But I don't know how to sample also across time so that the sample is done all over the interval of time that I have for each site (e.g. when snow was there, the lowest sites could have been checked before the highest sites, so the date of measurements are variable between sites).
Is someone familiar with ordinal data and time series? Or could someone give me some insights about how could I simplify my data and my analyses?
Hope that you understood something about my question and I'm open to any kind of suggestion. Thank you in advance!
Cheers,
Janisse
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I know, R is good, but you still have to write code to tell it what to do! If the data was collected in one season, then I would ignore 'date of measure' as a variable (treat it as a sub-sample), unless you measured in two seasons, in which case you can easily compare seasons :)
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One of my recent experiment refered to insect species, now the identification (to family level) has been done. In the following, I want to compare the differences in species richness and composition of insects between different treatments, which is easy. Besides, I also want to see the accumulative patterns of different functional groups (like herbivores vs. insect predators and pollinators vs. non-pollinators, or any other functional groups) in different treatments. However, I have few experiences in insect research and do not know how to identify which functional group an insect (family) belongs to. Does anyone know that? Are there some references or websites for such purposes?
I appreciate it a lot if anyone can give some suggestions.
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In insects there are many functional groups and according to the number of individuals registered in each evaluation date, you can organize them according to their feeding behavior that can pollinators, phytophages, granivores, predators, parasitoids, coprophagous, saprophagous, necrophagous, hematophagous, xylophagous, rizophagous, frugivorous, nocturnal, diurnal, aquatic or terrestrial etc.
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Hi,
I am wondering if, regarding a single natural ecosystem, herbivores (or rhizophages) belowground are more generalists (in their diets), than aboveground herbivores? Would the soil complexity tends to promote low specificity of root herbivores? Do you know any papers dealing with this topic?
Thanks in advance for your feedback?
Best,
Matthieu
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Assuming that u r a hardkeeper. you took 679 no. of animals to graze in the forest and field. using genetic analysis how can you group those animals? Lets say 19 animals are lost how can yo quantify them? Lets say there is an earthquake after 1 million years after, how can you say that how many animals are herbivores and howmany are carnivores? after 10 years of grazing the no. of species increased by 5 in no.s how?
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It's a hard question! I think if classification of species was done for the first time in our day using genetic analysis, the categories would be more fluid and lenient. I'm not a fan of evolution anyway
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Are there more efficient techniques available, rather than ImageJ, for quantifying herbivory damage from photos of leaves? I have a basic understanding of machine learning but don't want to spend too much time trying to learn another complicated technique.
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You could try LeafByte. It's a free and open source app for iPhones and iPads. It measures leaf area and herbivory levels much more quickly than ImageJ and related software, and it automatically saves your data for you in a spreadsheet. You can download it in the app store or read more about it at the website below.
Disclaimer-I was involved in making this app.
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Understanding the dietary requirements of a species is fundamental to its ex situ conservation.Green turtles are omnivores when young and become herbivores when they reach maturity, plant matter in the form of seaweed. Adult green turtles are herbivores, but in captivity the rescued turtles refuse to eat any other food, the primary food resource is not available , hence we are looking for preparing food resource which can help them to meet the nutritional requirement in their recovery from injuries.
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Seaweed based nutrition
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Phytophagous insects take longer decision making time compared with specialist herbivore during their host selection process?
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At least in Lepidoptera, it is generally the ovipositing female that selects the plant that the larvae will start on.
What sort of insect are you interested in and which life stage?
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I am trying to sequence microbiome of flour beetles (16s) but due to the flour diet - most of the reads are chloroplast reads (more than 90%) So far only V1-V2 region was sequenced. I am still waiting for the results of V3-V4 region
Is there any way to remove chloroplast DNA during DNA extraction from insects? I have read about speficic primers that deal with this problem but at the moment I am trying to explore all the possibilites. Thank you!
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Thank you very much. Unfortunately I wouldn´t use this protocol because I am working with flour beetles that are kept only on flour. For now, we won´t change the diet since we don´t know how would that affect our experiments and readouts.
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Phytophagous insects take longer decision making time compared with specialist herbivore during their host selection? How
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Thanks @ James Des Lauriers
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I am currently working on a project on herbivory and grasslands, but am unable to find proper review. Please help me in finding people who have done some sort of work in herbivory and grasslands management.
Best regards,
Shah
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Thank you Prof. HeinVan Gils and Prof. Lauchlan Hugh Fraser for your answers.
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We are working on a project “Grazing damage on agricultural grasslands caused by large wild herbivores”. We would like to know “If and how the damage on grasslands caused by ungulate grazing is treated (if it is assessed and evaluated) in EU countries?” We are interested in methodologies to see if some of  them can be used also in Slovenia. Thank you, Ida
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In my various research areas, I have not come across compensation legislation/regulation for grazing farmland by roe deer and/or red deer, the only widespread, wild, large ungulates in the EU.
As our colleagues have already mentioned, compensation for wild boar 'ploughing' is common and in the Netherlands compensation is paid for grazing by wild geese.
The current, controlled low deer densities in most of the EU seem to low to bother.
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This is an exciting project! We work on vanilla planifolia plantations in North-Eastern Madagascar & we have made many observations of ants on vanilla harvesting extra-floral nectar. Our project is called "Diversity Turn in Land Use Science" and the ecologists of our project are currently assessing the biodiversity on vanilla plantations and alternative land-use types in order to define the value of vanilla plantations for conservation. Our PhD student focusing on ants has collected ants via baiting and pitfall trapping. However, the topic with vanilla-ant mutualism is still a mystery to us - however pre-studies are needed to define common pest. However, our vanilla pest damage shows so far, that herbivory is seemingly minor problem. Looking forward to find out more about your project!
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In the analyze of ant-vanilla interaction it need to study not more ants, but the plant morphologie and the production by Vanilla of aromatic attractives by floral parts...
For exemple, by the Anther cap ... see my articles about DPU...
The animals in général have the possibility for change the place, the plants; and it need to see the relative immobilism of plants
Best regards
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I would like to calculate total amount of food that beetle larvae consume during larval stage. Unfortunately, they are soil dwellers by feeding on organic-matter rich soils. Feces can’t be distinguished from the food (soil). So, I used indirect methods to estimate their feeding performances.
I found that food retention time in the gut had linear relation with larval weight as:
R = 3W
where R is retention time (h) and W is larval weight (g)
and gut load (amount of food in larval body at a time) had linear relation with larval weight as:
L = 0.25W
where L is gut load (g) and W is larval weight (g).
The problem is beetle larval weight is not constant. It gradually increases over time. The growth of beetle larvae was varied in each individual and non-linear. Now, I have data about beetle growth for many individuals (the figure below is an example of the growth from one beetle). How can I estimate the total amount of food (soil) that each beetle eats during larval stage from these data?  
Thank you in advance.
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You may even go for secondary productivity. May be useful to you
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Field observations or microscopical analysis have provided abundant results for decades. Besides, these geese often feed on just a few species, such as Cyperaceae, Gramineae. Is there any necessity to identify these food items at species-level, if the food spectrum is always so narrow?
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I think geese can separate species, and they can also tell the difference within a species between plants that have a higher or lower quality (e.g. in nitrogen content). See e.g.
Stahl, J., A. J. Van Der Graaf, R. H. Drent, and J. P. Bakker. 2006. Subtle interplay of competition and facilitation among small herbivores in coastal grasslands. Functional Ecology 20:908-915.
But a full answer to your question depends on the objectives of your study, which are not fully clear to me
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I am doing herbivory experiments with T.ni caterpillars. I do have some susceptible and resistance plants variety. While arranging them in petriplate I think there should be some tricks. I mean patterns likewise suseptible should one side and resistance in other, or one by one?
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Our study focuses on the impacts of grazing on hydrological processes, mainly surface runoff, evapotranspiration, and soil loss. We study different animals (with soft-padded feet and hooves) and different grazing intensities, and focus on mountainous areas in Peru. We found empirical evidence in many regions of the world, but not comprehensive review that could support a simple modeling approach.Thanks in advance!
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Since you are here in California, you can see the massive hydrological changes in the Sierra foothills and the upper Sacramento River valley like around the town of Weed, or in the BLM lands north of Reno in the former wetland areas.  
By removing the perennial grasses, the annuals have been soil nutrient and soil organic matter miners, so large parts of the arid West that have been grazed for a period of time, are now nutrient and organic-matter starved.  
Soil has been starved by the cows and sheep to the point, that the nutrient levels are below levels needed by native seedlings to survive.  See pictures at http://www.ecoseeds.com/good.example.html, on the left is the flat with soil only and no nutrients added--the seeds sprouted and died of starvation.
For the acres of grasslands that I am currently restoring from Los Altos Hills to Capay Valley, we have to POUR the nutrients back into the soil, that have been removed by grazing, and also add back organic matter.  On one ranch, we have to add one ton of fertilizer per acre, mostly the calcium that was removed by the dairy operation in the milk that was produced there.
Until you rebuild a grassland ecosystem with diversity from scratch, you do not have a clue on what has been taken away by the cows, and how much you must put back.
Sincerely,  Craig Carlton Dremann
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Hello, 
I have been passed this photo of a small crustacean (Malacostraca?) eating planted mangrove seedlings (Rhizophora) in central coastal Vietnam. They are girdling the seedlings, which then fail. 
My knowledge does seem to be limited to: oh, looks like a sea louse (!), so I am asking the question.
The situation is somewhat brackish evidently, due to fluvial influence at that part of the estuary, and there is no herbivory in more saline  water plantings.
The picture isn't great, but hopefully enough. I do not expect there are easy solutions to the pest problem in mass reforestation efforts!
(Planted seedlings do seem to be generally more susceptible to herbivory and I do think, without visiting the site, that the mangrove species selection may be wrong here, but that is another topic!).
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Yes, there is debate about nurseries for the Rhizophoraceae, especially Rhizophora because the 'propagule' (viviparous seedling) is so easy to direct plant. The VN experience in reforesting after the US defoliation in Rung Sat (Can Gio now) and Ca Mau and continuing now in farmers planting in aquaculture areas was/is direct sowing. So easy.
Generally nursery culture is a waste BUT perhaps not in this case if the advanced seedlings are more resistant if grown on in a nursery. An avenue to try, although substitution of the first planted species in affected areas to Avicennia or Sonneratia might be better!? 
Gazi Bay is more saline I think, both being pretty open to the ocean and not having the same intensity of wet season, where everything turns fresh as here, even out to sea at the mouths of the rivers! 
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In the paper linked below a case study of a mason bee (Osmia bicornis) feeding on pollen is presented. We concluded that the growth and development and thus the fitness of the bee might be co-limited by the scarcity of N, K and Na in pollen. Cocoon production may be limited by a greater number of micronutrients. Since O. bicornis may experience limitations to the growth and development of its body and cocoon production because of the availability of certain elements in its food, the amounts of potentially limiting elements should be maximized during pollen collection by the adult female bee for its progeny.
Food nutritional quality is known to regulate populations of wild bees and may be a factor contributing to bee decline. In addition, specific micronutrients, especially Na and K, may be lacking in bee diets, thereby forcing bees to search for a balanced diet. The quality of the pollen diet has a known influence on the survival, physiology and life history traits of bees (of various taxa). These traits are all connected to fitness; therefore, pollen quality may influence bee foraging choices. Is it possible that the nutritional quality of pollen influences foraging behaviour and life-history traits of pollen-eaters? What do you think? 
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Indeed the variability of pollen nutritional value is related to environmental conditions only for euribionte - organism biologically versatile, adaptable to different environmental and nutritional conditions such as to permit the colonization of different habitats (contrary: stenobionte) - species. In particular conditions these forming so-called eco forms.
I am sorry, unfortunately I do not know a study to verify the hypothesis
Iuliana
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I'm trying to find work on non-mammal vertebrate herbivores to find methods to assess their impacts on native vegetation. Is anyone familiar with studies on this issue? 
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dear christina
we did some work on this on the island of la palma (canary islands) where introduced rabbits (and in former time also goats) and to a certain degree also barbary sheep (ammotragus lervia) are a great threat to native endemic plant species. some of them have decreased to only tiny remnant populations that are at the brink of extinction. some may have been lost in the past without anyone knowing about it. through exclosure experiments (fences) wherein native species are established, you can see the tremendous difference between vertebrate herbivory and the exclusion of it, making us aware how the island would look like if there were not rabiits, goat and sheep.
i attach the paper here.
best wishes
carl
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Hi everyone! Does anyone know about the herbivory/ovipository damage to plants that spider mites cause?- on a micro/molecular scale and on a whole plant basis. I am looking for literature or any kind of overview you can provide regarding the kind of damage that spider mites do to plants - both the kind of mechanical damage and the chemical if there is any. 
Thank you so much!
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I suggest that you read: The Ecology of Tetranychid Mites and Their Natural Control
C. B. Huffaker, M. van de Vrie, and J. A. McMurtry
Annual Review of Entomology Vol. 14 (1969): 125-174
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My colleagues are working on feeding preferences of macro symbionts of feather stars. They gathered data on stable isotopes from both sea lilies and its symbionts(shrimps, crabs, ,polychaetes, myzostomida etc). The results are quite surprising and not easy to interpret, so we want to have some reference points. Some people (who work with stable isotopes) advise us, that it might be more useful to collect data on primary consumers (not primary producents) from our area to have such a reference point.
But than we realized, that it is not an easy task to find really specialized primary consumer on the coral reef, as there is little known about food spectrum of most coral reefs inhabitant and many of them are mixotrophic.
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Hi Yury,
first of all, it would be important to match the stable isotopes data with gut content info. The primary consumers you are studying are filterfeeders, so they won't we strictly primary consumers. They are filtering POM, and Bacteria too. Therefore, as you indicated, they are all mixotrophic and probably, when you plot C vs N, you get a cloud of all species mixed with the chrinoids. So, this cloud is your base of "primary consumers" perhaps you could try to go upper from there. Like crabs and snails feeding on them and fishes. But, again, only stable isotopes is a weak info. You can match not only with gut content but also diving observations.
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We are interested in developing a new tool to quantify leaf herbivory, primarily by arthropods.  It will work from images taken of leaves in situ.  This will provide two advantages; leaves can be left in place without damaging the tree, and secondly it will allow for evaluation of damage over time.
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Hey Scott!  We have pretty much all the software in place now.  I guess the main question is how to sample the leaves.  Traditionally this seems to be done by removing them from the tree and analysing damage ex situ.  However, if we could image them on the tree we'd be able to do time-series analyses which would be more informative on several fronts.  We need to devise something like a little perspex holder with a scale that a leaf could be flattened on and photographed. Tree climbing equpiment would be essential too.  We're also working with Yubo Zhang in Stuart's group on canopy images to estimate forest biomass - this could be tied in.  Our main problem is time.  If you find someone interested in this we're happy to help supervise.
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We are currently doing a research on plant defense mechanism against caterpillar herbivory, and we would like to know if there are still possible ways to measure the effect of allelochemicals on caterpillars.
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Refer my research articles on allelopathy. View my publications on researchgate. 
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I have data consisting of seasonal transects of herbivore counts, which I wish to analyse using the kilometric abundance index. I want to determine how changes in prey abundance over the study period has affected demographic rates of various lion prides. I have used the outline of lion home ranges to divide the transects into transects per pride. However, due to seasonal changes in flooding and access to roads, some prides have more transects than others within each year. My main questions are:
1) How do I determine whether the differences in distance covered have a significant effect on the outcome of the kilometric abundance? And, if it does have an effect, how do I account for it?
2) I have both lean season and abundant season data for most years, but in two years have only abundant season data. If I want to use lean season data , how do I deal with the two years where I have only abundant season data?
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Had you tryied relative abundance?  ( relativize the abundance of each "sampling" per total km of that specific sample).  Then you can use any statistics that uses percentages. 
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I was watching a documentary from South Korea in which they are feeding domestic cats a vegan diet. I want to investigate if a vegan diet has negative impacts on carnivorous animals such as domestic cats.
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Grab two groups of cats and one of the feed groups with a vegetarian diet since they are born and the other a carnivorous diet and take medical data to see if there are significant differences, on the other hand you could also grab a group of carnivorous cats and submit durate a long time vegetarian diet to see differences between the before and after, the problem is to make them want to eat the food.
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I know of adult pest beetle (Popillia japonica and the mexican bean beetle) herbivory being negatively-affected by the treatment of leaflets with spider silk (Hlivko and Rypstra 2003; Rypstra and Buddle 2013). But I was wondering if there were any studies into pest species of Lepidoptera being affected.
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Hi Scott,
I don't know of any silk studies, but I wanted to suggest investigating repellency of spider frass. I would also suggest contacting John Sivinski with USDA-ARS in Gainesville, FL. I know he was very interested in this subject at one time. He just retired, but he may know of some good studies. Good luck!
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Hello to everybody. My study is focused on host preference of sucking herbivorous arthropods and, in particular, how plant leaf structural traits affect the feeding choice of herbivores. The information on how herbivores penetrate leaf tissue with their stylets (physical or enzymatic way) can explain some correlations of their densities with leaf structural and mechanical properties. Herbivores involved in my study are scale insects and mealybugs, aphids, whiteflies, thrips, and spider mites.
I can't find papers on feeding/probing behaviour of spider mites and the way they penetrate plant tissues. I would be grateful if anyone could recommend some publications regarding this.
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Dear Eugene,
The following book chapter is a decent place to start as it is a concise summary of about 20 years of work on the topic:
Tomczyk, A, Kropczyńska, D (1985) 1.4.7 Effects on the host plant. In: ‘Spider Mites: Their Biology, Natural Enemies and Control. Vol IA’. pp. 317-329. (Eds W Helle, MW Sabelis). (Elsevier: Amsterdam). World Crop Pests, 406 pp.
Briefly, penetration is physical, followed by injection of saliva, so both physical and enzymatic damage to cells occurs.
Kind regards, Owen.
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I was wondering whether in grasslands belowground herbivores are rather specific or generalist, and whether there are hypotheses stating that one or the other are more important for driving the assembly of plant communities. Any reference or idea is welcome!
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I would assume that it would be similar to above ground: some of both. I would also speculate that plants with foliar chemical defences would also exhibit similar root defences and so be fed on by specialists.
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I´m looking for a method to estimate plants biomass, maybe using plant cover? It is for understory species of a temperate forest under different silvopastoral practices.
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See:
Catchpole, W.R. and C.J. Wheeler. 2006. Estimating plant biomass: A review of techniques. Australian Journal of Ecology 17:121–131.
But you are correct that whatever method you use, calibration is important, and recalibration when making comparisons across times, treatments, gradients, etc.
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I'm trying to detect if reptiles eat plants looking to their drops, but it is really difficult to see plant material using magnifying lens if they are digested. So, do you know if there is any dye to detect the presence of plant material in faeces of vertebrates? If so, is there a protocol available? Thanks!
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To add to Lawrence's statement you could do an NDF acid wash, dissolving of all organic material except for structural carbohydrates - weigh faecal samples prior to acid wash, way NDF (neutral detergent fibre) after wash, difference is structural cellulose (plant lignin, etc). Will not allow you to measure non-structural plant material though.
With Zibani's suggestion, you need to add the markers to the plant material, collect the faeces, dry, grind, dissolve, and determine faecal marker concentrations via ICP analysis (remembering that very small amounts of marker elements such as Cr and Ti are present in all feed). In a controlled experiment with controlled feeding, this would be possible but not in the wild. Also, controlled feeding changes animal behaviour if it is unfamiliar to handling.
So many things to consider when doing what seems like a simple experiment!
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I am interested in running a leaf palatability experiment on a group of related daisies to see if there are any interesting patterns associated with leaf type and herbivory. I thought I could purchase snails which would not have been exposed to the native daisies I plan to work with, however I could really do with some feedback. Has anyone run a cafeteria type experiment in which random leaf types are pinned to a grid? Are there any good methods/publications out there? I am also interested in the type of vector used or available. How time consuming (sorry the pun) can it be? And is it fraught with other issues I should be aware of?
This is not something I am at all accustomed to (as you have noted), but I would really like to give it a go.
Feedback welcome!
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Dear Megan,
here is the protocol of an experiment I run a couple of years ago to test if different water treatments on grass affect palatability. Hope it helps!
Palatability test:
Material:
- petridishes
- leaf disc cutter
- Generalist herbivores (snail, caterpillar (E,g, spodoptera littoralis/exigua)
- fine balance
Method:
- Number petri dishes
- Determine herbivore fresh weight and put in petri dishes
- sample whole leaves (if you have enough leaves), put in moistened plastic bags and work fast to avoid excess transpiration
- take to balance table, cut 2 equally sized pieces of leaves and determine fresh weight of both immediately (one is the control leave, one the leaf herbivores feed on (test leave) (transpiration out of an leaf piece with cut ends is really fast, so try to work fast also)
- control leaf is dried and fresh weight/ dry weight ratio is determined
- test leave is given to herbivores, let them eat for at least 12 hours
- dry remaining test leaf after feeding
- use determined FW/DW ratio to determine consumed dry weight
- palatability= consumed dry weight/ herbivore FW prior to feeding
- or: just use consumed dry weight as response variable, and perform ANCOVA with herbivore fresh weight as a covariable (this is the preferable method perhaps, see Horton and Redak, Entom Exp Appl 69, 263-275, 1993)
- additionally you can weigh herbivores after feeding again, and then determine the relative growth rate RGR: gained weight/ [mean biomass of herbivore]*time interval
or see: Wardle et al. 1998, Can comparative approaches based on plant ecophysiological traits predict the nature of biotic
interactions and individual plant species effects in
ecosystems, Journal of Ecology 86, 405-420.
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Wondering if somebody has quantitative data for observations on ants attacking herbivores and/or pollinators (as # observations/period of time) without any sort of manipulation. In other words, a person sits, observes, and records a natural predation event involving insects. There is interesting research on predation by (e.g.) spiders or ants, but it seems obvious that conclusions are mostly based on the results of removing the predator (either naturally not present in some plants, but present in others or experimentally removed) and measuring the effects of this onto a variety of plant features (involving vegetative growth or reproduction). Is this all what we have? Can anecdotal observations only be counted with one hand?
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Thank you for the paper Andre. I like this kind of intensive field-work experimentation...
I found an interesting paper on pure observational data for ambush predation (ant attacking pollinators). [Rodriguez-Girones et al. 2013 Journal of Ecology 101, 1000-1006. -in case the link is not working-]. I believe that observing events like predation, 100% un-manipulated are a jewel, something that triggers some lines of investigation.