This document summarises the Round 1 - Initial estimates of the ACT Urban Habitat and Connectivity Project expert elicitation for small to medium terrestrial mammals using the IDEA protocol (refer to Hemming et al. 2018 “A practical guide to structured expert elicitation using the IDEA protocol” and Burgman 2016 “Trusting Judgements: How to get the best out of experts”).
For each question asked in the expert elicitation, we have summarised the results. All responses from the expert elicitation remain anonymous, with visualised experts estimates being denoted by a number on the x- axis. Below each visualised estimate, the comments provided by experts are collated.
The intervals displayed are for a Three-Step Elicitation.
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The next series of visualisations relate to structural habitat metrics.
Structural habitat metrics describe how the various elements of a species’ habitat are arranged in space. For example, some arboreal species may need tree canopies a certain distance apart to be able to successfully navigate from one to the next. Another species might require grass heights of a certain amount to escape predation, whilst another species might only be able to persist within a certain distance from a water body.
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This could be related to the amount of shade the taxon group prefers or is tolerant of in its preferred habitat, the distance an arboreal species can move from one tree to the next without going along the ground, or some other feature of the taxon groups’ general biology or life history. This metric considers the availability of both exotic and native tree species in the environment, as well as both young and mature trees (> 3m height). The answer to this question will give an equivalent score to something like “percentage canopy cover”, which might be a more familiar (but harder to map) version of this metric.
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 2 | 1.0 | 10 | This is really hard, as it really will vary a lot between gliding, arboreal and semi-arboreal mammals, so I went with something that arboreal mammals could probably cope with | 60 | Small_medium_terrestrial_mammal | tree_canopy | Initial |
| 40 | 10 | 5.0 | 20 | As you point out - I am more familiar with thinking about % canopy cover or stem density in a defined area rather than preferred canopy distances. Rough estimates based on small ground dwelling species benefiting from higher cover (low) and gliders actually requiring some distance (high) | 30 | Small_medium_terrestrial_mammal | tree_canopy | Initial |
| 41 | 1 | 0.0 | 1 | For arboreal species such as possums, to avoid predation will need to travel between trees without climbing down one tree and up the next. The canopies must be within 1m of each other for this to be possible. | 90 | Small_medium_terrestrial_mammal | tree_canopy | Initial |
| 42 | 50 | 0.0 | 200 | Based on field observations for most species and surveys done for bandicoots. | 60 | Small_medium_terrestrial_mammal | tree_canopy | Initial |
| 43 | 10 | 5.0 | 100 | CSIRO Studies in Brindabella Ranges indicate some native small mammals are reluctant to cross fire trails of 5m width, even in dense wet forest. This may be due to canopy gaps or more plausibly understory or ground cover gaps. | 25 | Small_medium_terrestrial_mammal | tree_canopy | Initial |
| 45 | 0 | 0.0 | 2 | Ideally arboreal mammals would move tree to tree without having to jump as it can be risky and also leaves them exposed to predators. Similar risks for ground dwelling mammals being sighted by birds of prey or their rest spots being affected by extreme heat from exposure however still allowing filtered light | 75 | Small_medium_terrestrial_mammal | tree_canopy | Initial |
| 47 | 20 | 1.0 | 50 | Cover and fallen debris/timber for species like Antechinus and suitable gliding distance for feathertail gliders | 50 | Small_medium_terrestrial_mammal | tree_canopy | Initial |
| 48 | 10 | 0.0 | 200 | Common Wombat probably prefers greater tree spacing (hence more grass) than I indicated. Also I disregarded Eastern Quoll which lives far from trees in some cases. | 5 | Small_medium_terrestrial_mammal | tree_canopy | Initial |
| 49 | 3 | 1.0 | 23 | My decision is based on working in the NSW and ACT region, where I observed that this taxon group were more commonly seen in habitat patches with 2-5 m between tree canopies. This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. This work hasn’t been published yet. | 60 | Small_medium_terrestrial_mammal | tree_canopy | Initial |
| Aggregated | 12 | 1.4 | 67 | NA | 51 | Small_medium_terrestrial_mammal | tree_canopy | Aggregated |
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This relates to the composition of the urban forest or remnant woodland in terms of native and exotic trees. What percentage of trees need to be native for an area to be suitable habitat for this species group? This will relate to things such as food availability or the year-round availability of canopy cover. For some species, only native trees will be beneficial whilst other species might happily utilise any tree species as part of core habitat structure.
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 70 | 30 | 80 | Again this will vary a lot depending on whether the species requires hollows (typically only in natives), natives to feed on (e.g. koalas), or not. | 60 | Small_medium_terrestrial_mammal | native_trees | Initial |
| 40 | 66 | 50 | 80 | Idea is that non-native trees can provide the needed structure (habitat, shelter, protection from predators) and potentially food resources but as a component of a native dominated ecosystem. My direct experience with this Q relates to exotic dominated understory facilitating higher small mammal abundance, but this was within the context of a groundlayer that still comprised native species, and an intact tree and canopy layer that was 100% native. So some but not too much maybe :) | 30 | Small_medium_terrestrial_mammal | native_trees | Initial |
| 41 | 80 | 50 | 100 | For nutrition (leaves, nectar) and shelter (hollows), large and old native trees will provide for their needs better than non-native species. | 90 | Small_medium_terrestrial_mammal | native_trees | Initial |
| 42 | 85 | 50 | 100 | Based on field observations for most species and surveys done for bandicoots. | 70 | Small_medium_terrestrial_mammal | native_trees | Initial |
| 43 | 50 | 25 | 75 | Total guess | 5 | Small_medium_terrestrial_mammal | native_trees | Initial |
| 45 | 70 | 60 | 80 | I think this really depends on the density of individuals and species in the area and depends on how much competition for resources in that area. | 50 | Small_medium_terrestrial_mammal | native_trees | Initial |
| 47 | 50 | 30 | 100 | Thinking about the provision of hollows, but this also depends greatly on the types of exotic trees present. If alellopathic species are present, these will greatly reduce understorey cover to the detriment of native small to medium mammals | 60 | Small_medium_terrestrial_mammal | native_trees | Initial |
| 48 | 100 | 0 | 100 | Dasyurus viverrinus and Bettongia gaimardi live in pine plantations with almost 100% non-native trees. I have no way of knowing about the others. | 5 | Small_medium_terrestrial_mammal | native_trees | Initial |
| 49 | 90 | 50 | 98 | My decision is based on working in the NSW and ACT region, where I observed that this taxon group were more commonly seen in habitats dominant by native species in communities such as box-gum grassy woodlands. This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. This work hasn’t been published yet. | 60 | Small_medium_terrestrial_mammal | native_trees | Initial |
| Aggregated | 73 | 38 | 90 | NA | 48 | Small_medium_terrestrial_mammal | native_trees | Aggregated |
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This relates to the composition of the urban forest or remnant woodland in terms of native and exotic trees. What percentage of trees need to be native for an area to be suitable habitat for this species group? This will relate to things such as food availability or the year-round availability of canopy cover. For some species, only native trees will be beneficial whilst other species might happily utilise any tree species as part of core habitat structure.
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 5 | 1 | 10 | As before with other estimate re: canopy | 60 | Small_medium_terrestrial_mammal | mature_trees | Initial |
| 40 | 10 | 5 | 20 | Same sort of logic as Q1. Almost the same Q so for now I’ll just answer the same | 30 | Small_medium_terrestrial_mammal | mature_trees | Initial |
| 41 | 30 | 10 | 100 | Mature trees need to be close enough together to provide cover and debris, while not preventing growth of grasses for ground-dwelling mammals to forage in. | 70 | Small_medium_terrestrial_mammal | mature_trees | Initial |
| 42 | 100 | 10 | 200 | Based on field observations for most species and surveys done for bandicoots. | 60 | Small_medium_terrestrial_mammal | mature_trees | Initial |
| 43 | 30 | 20 | 100 | I think I remember some glider species requiring large trees to be around 25m apart and no more than 100m | 25 | Small_medium_terrestrial_mammal | mature_trees | Initial |
| 45 | 50 | 15 | 100 | I am not confident in my estimate as it depends on may factors including competition. Urban densities would vary a lot compared with populations and people providing shelter either directly or indirectly | 25 | Small_medium_terrestrial_mammal | mature_trees | Initial |
| 47 | 20 | 10 | 50 | for provision of hollows, but especially for contribution to ground layer debris and cover | 50 | Small_medium_terrestrial_mammal | mature_trees | Initial |
| 48 | 20 | 20 | 100 | I really dont know | 5 | Small_medium_terrestrial_mammal | mature_trees | Initial |
| 49 | 10 | 8 | 30 | My decision is based on working in the NSW and ACT region, where I observed that this taxon group were more commonly seen in habitats with many mature trees (distance varies in different communities) with fallen timber on the ground. This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. This work hasn’t been published yet. | 55 | Small_medium_terrestrial_mammal | mature_trees | Initial |
| Aggregated | 31 | 11 | 79 | NA | 42 | Small_medium_terrestrial_mammal | mature_trees | Aggregated |
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This metric might reflect the overall amount of mid-storey cover (0.5 – 3m height) required by a taxon group, or how far they can move between shrubs. This metric considers the availability of both exotic and native mid-storey species in the environment. The answer to this question will give an equivalent score to something like “percentage mid-storey canopy cover”, which might be a more familiar (but harder to map) version of this metric.
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 3.0 | 1.0 | 10 | Again, will depend on whether species are obligate arboreal species or not | 60 | Small_medium_terrestrial_mammal | mid_canopy | Initial |
| 40 | 2.0 | 0.0 | 10 | Slightly higher confidence as my own experience and knowledge of the literature here is that the more is always better more or less….. Will typically get way more small mammals where understory is dense and heterogenous | 60 | Small_medium_terrestrial_mammal | mid_canopy | Initial |
| 41 | 5.0 | 1.0 | 10 | Ground-dwelling species like native rodents and antechinus (for example) need patches of mid-story to shelter in to avoid predation. Connectivity between these patches will be important for their dispersal and survival. | 70 | Small_medium_terrestrial_mammal | mid_canopy | Initial |
| 42 | 10.0 | 0.0 | 100 | Based on field observations for most species and surveys done for bandicoots. Some species prefer more open (e.g. wombats), other prefer cover. Hard to generalise | 80 | Small_medium_terrestrial_mammal | mid_canopy | Initial |
| 43 | 10.0 | 5.0 | 50 | See comment on question 1 - CSIRO study found Antechinus sp. reluctant to cross a 5m wide fire trail in Brindabella Ranges in the ACT | 20 | Small_medium_terrestrial_mammal | mid_canopy | Initial |
| 45 | 20.0 | 5.0 | 50 | This answer is based on shelter (especially for ground dwelling animals) and food availability | 50 | Small_medium_terrestrial_mammal | mid_canopy | Initial |
| 47 | 10.0 | 1.0 | 20 | Based on a knowledge of ground-dwelling small mammals | 60 | Small_medium_terrestrial_mammal | mid_canopy | Initial |
| 48 | 10.0 | 0.0 | 30 |
Antechinus agilis, Antechinus flavipes, Bettongia gaimardi, Dasyurus maculatus, Dasyurus viverrinus, Perameles nasuta, Sminthopsus murina, Vombatus ursinus Thinking mainly of Antechinus |
5 | Small_medium_terrestrial_mammal | mid_canopy | Initial |
| 49 | 7.0 | 1.0 | 10 | My decision is based on working in the NSW and ACT region, where I observed that this taxon group were more commonly seen in habitats with low shrub cover percentage. This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. This work hasn’t been published yet. | 50 | Small_medium_terrestrial_mammal | mid_canopy | Initial |
| Aggregated | 8.6 | 1.6 | 32 | NA | 51 | Small_medium_terrestrial_mammal | mid_canopy | Aggregated |
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This metric might reflect the overall amount of mid-storey cover (0.5 – 3m height) required by a taxon group, or how far they can move between shrubs. This metric considers the availability of both exotic and native mid-storey species in the environment. The answer to this question will give an equivalent score to something like “percentage mid-storey canopy cover”, which might be a more familiar (but harder to map) version of this metric.
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 50 | 10 | 90 | I’m basing this mostly on structure and not a strong reliance as food plants | 60 | Small_medium_terrestrial_mammal | native_mid | Initial |
| 40 | 50 | 0 | 100 | I’m being a little unhelpful with this Q as: Low estimate == small mammals can be cool with a completely exotic mid-storey, depending on context. High estimate == while some exotics may provide resources potentially required for persistence in a modified landscape, I’m unaware of research that has explicitly tested that (so beyond just an association). So conventional wisdom is that native mammals should not require any exotic resources to persist (100% native). Best == mid point of extremes that are potentially just as viable. | 100 | Small_medium_terrestrial_mammal | native_mid | Initial |
| 41 | 80 | 50 | 100 | While non-native mid-story may provide similar structure to native mid-story, there are cases where non-native shrubs can provide inappropriate food resources, and drain more resources (e.g. moisture) from their patch to the detriment of other native species. | 50 | Small_medium_terrestrial_mammal | native_mid | Initial |
| 42 | 85 | 50 | 100 | Based on field observations for most species and surveys done for bandicoots. | 60 | Small_medium_terrestrial_mammal | native_mid | Initial |
| 43 | 25 | 10 | 50 | Guess! But I would think the presence of at least SOME native shrubs would be important for native small mammals. | 5 | Small_medium_terrestrial_mammal | native_mid | Initial |
| 45 | 80 | 60 | 100 | 0 | 50 | Small_medium_terrestrial_mammal | native_mid | Initial |
| 47 | 40 | 1 | 70 | Structure is most important, so depends of the physical structure of the shrubs. Overall diversity is also important, if just one species of exotic shrub this estimate should be reduced for example | 50 | Small_medium_terrestrial_mammal | native_mid | Initial |
| 48 | 30 | 0 | 50 |
Assumed ‘native’ was unintentionally omitted from the question. Antechinus agilis, Antechinus flavipes, Bettongia gaimardi, Dasyurus maculatus, Dasyurus viverrinus, Perameles nasuta, Sminthopsus murina, Vombatus ursinus I suspect structure is much more important than floristic composition for these species |
10 | Small_medium_terrestrial_mammal | native_mid | Initial |
| 49 | 90 | 70 | 98 | My decision is based on working in the NSW and ACT region, where I observed that this taxon group were more commonly seen in habitats with many native shrubs with fallen timber on the ground. This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. This work hasn’t been published yet. | 60 | Small_medium_terrestrial_mammal | native_mid | Initial |
| Aggregated | 59 | 28 | 84 | NA | 49 | Small_medium_terrestrial_mammal | native_mid | Aggregated |
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This metric enables mapping of the potential distribution for those species which are tied in some way to ground layer vegetation. This might be a small species which lives within the grass layer (e.g. invertebrates, reptiles) or a larger species which relies on grass as food (e.g. kangaroos). How far will this taxon group be found from ground-layer vegetation?
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 5 | 3 | 10 | There will be big differences between species and their willingness to move away from vegetation, e.g. a native rodent may not go as far as a wallaby. | 60 | Small_medium_terrestrial_mammal | ground_layer | Initial |
| 40 | 0 | 0 | 0 |
I’m assuming this Q relates to groundlayer vegetation / bare ground dynamics? Having not worked on mammals in grasslands I have not given any thought to this kind of small-scale veg-animal interaction. Perhaps the answer is actually just zero as in the preferred distance from ground layer veg is “I never want to be away from ground layer veg ever”. Maybe this could be recontextualised as like “minimum tolerable % cover”. Depends on whether I’ve missed the point of this metric. Also I have not been considering kangaroos in my thinking at all – surely not a small-medium sized mammal :) |
100 | Small_medium_terrestrial_mammal | ground_layer | Initial |
| 41 | 95 | 90 | 100 | With the remaining 5-10% being rocky outcrops, this taxon group requires well-connected ground-layer vegetation. | 90 | Small_medium_terrestrial_mammal | ground_layer | Initial |
| 42 | 10 | 10 | 100 | Based on field observations for most species and surveys done for bandicoots. | 60 | Small_medium_terrestrial_mammal | ground_layer | Initial |
| 43 | 5 | 5 | 20 | See previous comment on CSIRO study of small mammals in Brindabella Ranges. | 10 | Small_medium_terrestrial_mammal | ground_layer | Initial |
| 45 | 20 | 3 | 50 | the larger distance is based on larger animals | 50 | Small_medium_terrestrial_mammal | ground_layer | Initial |
| 47 | 2 | 0 | 10 | This depends on the amount of cover other than vegetation. Estimates are presuming bare earth around vegetation | 60 | Small_medium_terrestrial_mammal | ground_layer | Initial |
| 48 | 0 | 0 | 0 |
Antechinus agilis, Antechinus flavipes, Bettongia gaimardi, Dasyurus maculatus, Dasyurus viverrinus, Perameles nasuta, Sminthopsus murina, Vombatus ursinus Ground layer vegetation is extremely important for nearly all of these and even crossing a fire road is probably a serious undertaking in some cases. I used zero here to indicate they prefer to be no distance from ground layer vegetation. |
10 | Small_medium_terrestrial_mammal | ground_layer | Initial |
| 49 | 1 | 0 | 5 | My decision is based on working in the NSW and ACT region, where I observed that this taxon group were more commonly seen in habitats with bare groun or ground covered by leaf litter with fallen timber on the ground. This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. This work hasn’t been published yet. | 55 | Small_medium_terrestrial_mammal | ground_layer | Initial |
| Aggregated | 15 | 12 | 33 | NA | 55 | Small_medium_terrestrial_mammal | ground_layer | Aggregated |
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This metric relates to the composition of the ground storey vegetation (grasses, rushes, forbs, sedges; < 0.5m height). What is the percentage of the ground layer vegetation which needs to be native to provide suitable habitat for this taxon group?
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 70 | 20 | 100 | Species dependent | 60 | Small_medium_terrestrial_mammal | native_ground | Initial |
| 40 | 50 | 30 | 70 | Not confident for reasons described in previous answer, so have sat on the fence. Logic being (1) I’m not experienced or well read in what small mammals are doing in woodlands with exotic dominated ground covers. (2) Its my impression that there those kinds of woodlands rarely have any native small mammals. (3) But that is probably due to other threats (surrounding land-use, invasive predators) (4) so like an exotic dominated midstory being completely fine in an otherwise native-dominated community, exotic ground cover could also be completely fine (providing necessary structure etc) so long as other things are good (plenty of CWD, native shrubs, etc,) Argh context | 10 | Small_medium_terrestrial_mammal | native_ground | Initial |
| 41 | 75 | 50 | 90 | Structurally non-native ground-layer vegetation may provide connective habitat for dispersal, but is not likely to provide appropriate food for grass and seed-eaters. | 80 | Small_medium_terrestrial_mammal | native_ground | Initial |
| 42 | 90 | 50 | 100 | Based on field observations for most species and surveys done for bandicoots. | 80 | Small_medium_terrestrial_mammal | native_ground | Initial |
| 43 | 25 | 10 | 50 | Guess | 5 | Small_medium_terrestrial_mammal | native_ground | Initial |
| 45 | 75 | 40 | 100 | lower estimate is based on some exotics being suitable for some species | 50 | Small_medium_terrestrial_mammal | native_ground | Initial |
| 47 | 75 | 50 | 100 | Diversity is most important here | 50 | Small_medium_terrestrial_mammal | native_ground | Initial |
| 48 | 10 | 0 | 20 |
Antechinus agilis, Antechinus flavipes, Bettongia gaimardi, Dasyurus maculatus, Dasyurus viverrinus, Perameles nasuta, Sminthopsus murina, Vombatus ursinus Structure matters more than floristics |
10 | Small_medium_terrestrial_mammal | native_ground | Initial |
| 49 | 90 | 50 | 98 | My decision is based on working in the NSW and ACT region, where I observed that this taxon group were more commonly seen in habitats dominant by native ground layer vegetation. This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. This work hasn’t been published yet. | 60 | Small_medium_terrestrial_mammal | native_ground | Initial |
| Aggregated | 62 | 33 | 81 | NA | 45 | Small_medium_terrestrial_mammal | native_ground | Aggregated |
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This metric relates to the average height (excluding seed stalks or other reproductive structures) of grasses, sedges, rushes, forbs and other ground layer vegetation. It might affect things like the availability of food sources (e.g. grass seeds) or opportunities for small animals to escape from predators. What is the minimum height of ground layer vegetation that provides suitable habitat for this taxon group?
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 50 | 30.0 | 100 | Most species will want a mix of tall and thick vegetation and open patches | 75 | Small_medium_terrestrial_mammal | min_height_ground | Initial |
| 40 | 10 | 8.0 | 15 | None | 50 | Small_medium_terrestrial_mammal | min_height_ground | Initial |
| 41 | 20 | 10.0 | 30 | Small mammals require enough cover to provide shelter and protection from predators, without having light filtered due to thick, high ground-layer vegetation (especially for nocturnal mammals). | 90 | Small_medium_terrestrial_mammal | min_height_ground | Initial |
| 42 | 30 | 2.0 | 50 | Based on field observations for most species and surveys done for bandicoots. | 60 | Small_medium_terrestrial_mammal | min_height_ground | Initial |
| 43 | 25 | 5.0 | 50 | Guess but needs to provide some cover for small mammals. Figures are in cm. | 5 | Small_medium_terrestrial_mammal | min_height_ground | Initial |
| 45 | 20 | 5.0 | 30 | this lower height estimate is based on thing like potoroos being able to move safely through grass while still being sheltered | 50 | Small_medium_terrestrial_mammal | min_height_ground | Initial |
| 47 | 20 | 10.0 | 30 | this estimate based on smaller ground dwelling mammals like antechinus | 75 | Small_medium_terrestrial_mammal | min_height_ground | Initial |
| 48 | 10 | 2.0 | 20 | Antechinus agilis, Antechinus flavipes, Bettongia gaimardi, Dasyurus maculatus, Dasyurus viverrinus, Perameles nasuta, Sminthopsus murina, Vombatus ursinus | 10 | Small_medium_terrestrial_mammal | min_height_ground | Initial |
| 49 | 5 | 1.0 | 10 | My decision is based on working in the NSW and ACT region, where I observed that this taxon group were more commonly seen in habitats with 5 cm grass height. This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. This work hasn’t been published yet. | 60 | Small_medium_terrestrial_mammal | min_height_ground | Initial |
| Aggregated | 21 | 8.1 | 37 | NA | 53 | Small_medium_terrestrial_mammal | min_height_ground | Aggregated |
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As above, but this time please describe the maximum height of ground layer vegetation that provides suitable habitat for this taxon group? It might affect things like the ability of a species to effectively move through ground layer vegetation, or find suitable burrowing sites, or access to solar radiation.
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 80 | 30 | 100 | Similar to before | 70 | Small_medium_terrestrial_mammal | max_height_ground | Initial |
| 40 | 24 | 20 | 30 | None | 50 | Small_medium_terrestrial_mammal | max_height_ground | Initial |
| 41 | 40 | 30 | 50 | Small mammals require enough cover to provide shelter and protection from predators, without having light filtered due to thick, high ground-layer vegetation (especially for nocturnal mammals). | 90 | Small_medium_terrestrial_mammal | max_height_ground | Initial |
| 42 | 50 | 30 | 120 | Based on field observations for most species and surveys done for bandicoots. | 60 | Small_medium_terrestrial_mammal | max_height_ground | Initial |
| 43 | 0 | 0 | 0 | 0 | 0 | Small_medium_terrestrial_mammal | max_height_ground | Initial |
| 45 | 60 | 50 | 80 | while grass gives shelter it can also make it hard to move freely if it too think and long however it needs to be long enough to build nests | 50 | Small_medium_terrestrial_mammal | max_height_ground | Initial |
| 47 | 40 | 30 | 50 | Density is the most important aspect to reducing movement rather than height | 40 | Small_medium_terrestrial_mammal | max_height_ground | Initial |
| 48 | 50 | 20 | 100 |
Antechinus agilis, Antechinus flavipes, Bettongia gaimardi, Dasyurus maculatus, Dasyurus viverrinus, Perameles nasuta, Sminthopsus murina, Vombatus ursinus Bettongs avoid dense tall ground layer veg. Probably inhibits the two Dasyurus too. |
10 | Small_medium_terrestrial_mammal | max_height_ground | Initial |
| 49 | 30 | 20 | 50 | My decision is based on working in the NSW and ACT region, where I observed that this taxon group were more commonly seen in habitats with 30 cm small shrub height. This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. This work hasn’t been published yet. | 55 | Small_medium_terrestrial_mammal | max_height_ground | Initial |
| Aggregated | 42 | 26 | 64 | NA | 47 | Small_medium_terrestrial_mammal | max_height_ground | Aggregated |
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This metric enables mapping of the potential distribution for those species which are tied in some way to a permanent waterbody. This might be a small species which is semi-aquatic (e.g. some frogs, turtles) or a larger species which relies on permanent water to drink (e.g. some birds and mammals). How far will this taxon group be found from permanent water?
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 1000 | 50 | 5000 | Many mammals don’t need water to drink, but some do (e.g. wallabies). I’m assuming rakali are not being considered here. Some mammals could move a long distance to and from water if needs be. | 60 | Small_medium_terrestrial_mammal | waterbody | Initial |
| 40 | 0 | 0 | 0 | Not a requirement I reckon. But that assessment is not based on really anything other than experience in the field (I couldn’t tell you were the closest water body was for sites I’ve monitored small mammals on) and knowledge of the literature (I dont recall seeing this metric considered in small mammal research) | 50 | Small_medium_terrestrial_mammal | waterbody | Initial |
| 41 | 100 | 20 | 300 | For smaller mammals, they will be limited in the distance they can reasonably travel to access water. This is especially pertinent in our drought-prone landscape. | 70 | Small_medium_terrestrial_mammal | waterbody | Initial |
| 42 | 1000 | 100 | 2000 | Based on field observations for most species and surveys done for bandicoots. | 60 | Small_medium_terrestrial_mammal | waterbody | Initial |
| 43 | 0 | 0 | 0 | 0 | 0 | Small_medium_terrestrial_mammal | waterbody | Initial |
| 45 | 300 | 25 | 1000 | much smaller animals would need to be closer however larger species may be able to travel larger distances. this would change between summer and winter | 30 | Small_medium_terrestrial_mammal | waterbody | Initial |
| 47 | 0 | 0 | 0 | Can’t think of any small to medium mammals necessarily tied to waterbodies | 50 | Small_medium_terrestrial_mammal | waterbody | Initial |
| 48 | 3000 | 1000 | 5000 |
Antechinus agilis, Antechinus flavipes, Bettongia gaimardi, Dasyurus maculatus, Dasyurus viverrinus, Perameles nasuta, Sminthopsus murina, Vombatus ursinus Thinking here of Wombat |
10 | Small_medium_terrestrial_mammal | waterbody | Initial |
| 49 | 0 | 0 | 0 | My decision is based on working in the NSW and ACT region, where I observed that this taxon group were more commonly seen in habitats close to water body. But no direct connectivty hasnt been found by my research. This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. This work hasn’t been published yet. | 50 | Small_medium_terrestrial_mammal | waterbody | Initial |
| Aggregated | 600 | 133 | 1478 | NA | 42 | Small_medium_terrestrial_mammal | waterbody | Aggregated |
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The next series of visualisations relate to non-structural habitat metrics.
This section asks questions regarding the non-structural elements which dictate habitat suitability for each taxon group. These includes things such as the amount of light which is tolerable at the time the species is active, or appropriate thermal conditions.
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This metric relates to the maximum tolerable light level which is associated with suitable habitat for this taxon group. It relates to the amount of artificial light provided at night in the urban environment (e.g from streetlights, or buildings). For some species, artificial light may disrupt foraging behaviours, mate finding behaviours, or circadian rhythm.
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 5.0 | 0.1 | 10 | So species dependent | 50 | Small_medium_terrestrial_mammal | night_light | Initial |
| 40 | 1.0 | 0.1 | 5 | No direct experience and have only seen research on the impacts of urban lighting on bats. From memory, even low levels of artificial light can majorly disrupt microbat movement and behaviour. Alterantively, large bats use road lighting to navigate and establish flyways over highways. I know we’re only interested in terrestrial mammals. But not really sure | 10 | Small_medium_terrestrial_mammal | night_light | Initial |
| 41 | 2.0 | 0.1 | 5 | For this taxon group which is dominated by nocturnal species, nighttime light will be a limiting factor in their ability to forage and hunt. Streetlights will prevent movement and increase the risk of predation. | 90 | Small_medium_terrestrial_mammal | night_light | Initial |
| 42 | 0.1 | 0.0 | 1 | Based on field observations for most species and surveys done for bandicoots. | 60 | Small_medium_terrestrial_mammal | night_light | Initial |
| 43 | 0.0 | 0.0 | 0 | I have no idea, | 0 | Small_medium_terrestrial_mammal | night_light | Initial |
| 45 | 7.0 | 5.0 | 15 | This is based on some species benefiting from street lights while others do not | 50 | Small_medium_terrestrial_mammal | night_light | Initial |
| 47 | 10.0 | 1.0 | 20 | type of light (spectrum) important | 50 | Small_medium_terrestrial_mammal | night_light | Initial |
| 48 | 10.0 | 5.0 | 100 | Antechinus agilis, Antechinus flavipes, Bettongia gaimardi, Dasyurus maculatus, Dasyurus viverrinus, Perameles nasuta, Sminthopsus murina, Vombatus ursinus | 5 | Small_medium_terrestrial_mammal | night_light | Initial |
| 49 | 0.0 | 0.0 | 0 | My decision is based on working in the NSW and ACT region. Usually we found native species in non-residential areas. So I assume low night-time light would be ideal. | 40 | Small_medium_terrestrial_mammal | night_light | Initial |
| Aggregated | 3.9 | 1.3 | 17 | NA | 39 | Small_medium_terrestrial_mammal | night_light | Aggregated |
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This metric relates to the maximum ambient temperature which is associated with suitable habitat for this taxon group. Ambient temperature is the temperature which a mercury thermometer would record if it was suspended in the air out of direct sunlight (e.g. in the shade). This metric is likely to be relevant to larger terrestrial species, such as kangaroos, as well as arboreal species such as birds and bats.
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 40 | 39 | 50 | Susceptibility to heat stress will vary widely amongst mammals | 60 | Small_medium_terrestrial_mammal | ambient_temp | Initial |
| 40 | 0 | 0 | 0 | None | 0 | Small_medium_terrestrial_mammal | ambient_temp | Initial |
| 41 | 37 | 35 | 39 | Above 40 degrees, thermoregulation becomes difficult for furred small mammals. For flying-foxes (not considered in my estimate), temperatures above 38 cause significant heat stress, and above 40 can cause heat stroke and death. | 80 | Small_medium_terrestrial_mammal | ambient_temp | Initial |
| 42 | 45 | 35 | 50 | Not sure if this relates to a short spike in temp, or longer periods. Spp likely to mitigate against short term spikes by sheltering in cooler locations but longer periods could impact their ability to feed, move, breed. | 70 | Small_medium_terrestrial_mammal | ambient_temp | Initial |
| 43 | 43 | 43 | 43 | 43 deg seems to be the threshold for some fruit bats. You may like to check with others regarding maximum overnight temperatures for Greater Gliders. From memory its up around 28 deg - over which they loose body mass due to energetic balance going to thermoregulation (cooling) and they can’t keep food up to support this. | 50 | Small_medium_terrestrial_mammal | ambient_temp | Initial |
| 45 | 38 | 30 | 50 | this is based on different thresholds and some animals ability to burrow | 40 | Small_medium_terrestrial_mammal | ambient_temp | Initial |
| 47 | 25 | 0 | 40 | In antechinus temperature during development can influence metabolism, and this is probably really important for semelparous species | 50 | Small_medium_terrestrial_mammal | ambient_temp | Initial |
| 48 | 0 | 0 | 0 | Antechinus agilis, Antechinus flavipes, Bettongia gaimardi, Dasyurus maculatus, Dasyurus viverrinus, Perameles nasuta, Sminthopsus murina, Vombatus ursinus | 5 | Small_medium_terrestrial_mammal | ambient_temp | Initial |
| 49 | 35 | 30 | 42 | My decision is based on working in the NSW and ACT region and weather in the past 4-5 years. This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. This work hasn’t been published yet. | 60 | Small_medium_terrestrial_mammal | ambient_temp | Initial |
| Aggregated | 29 | 24 | 35 | NA | 46 | Small_medium_terrestrial_mammal | ambient_temp | Aggregated |
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The next series of visualisations relate to habitat patch size and typical dispersal distances.
This section asks questions regarding habitat patch sizes and typical dispersal distances for your selected taxon group.
Habitat patch size is explored for both core habitat (where the species lives full time) and corridors (areas the species might move through when dispersing, or when moving between connected habitat patches). Dispersal capability covers how far a species will typically move within and between habitat patches (e.g. within a home range), as well as how far they typically will move during a major dispersal event, e.g. when migrating or dispersing to a new home range.
The answers to these questions will help us to understand how far apart different patches of habitat can be whilst still being connected for a taxon group, as well as what the aspirations should be in terms of the total extent of connected habitat at the landscape or regional scale to facilitate typical dispersal patterns for the species. Below, we ask you to provide your upper, lower and best estimates for a range of metrics related to patch size and movement behaviour.
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This metric relates to the minimum dimensions of an area which could be considered suitable core habitat for the taxon group. By core habitat, this would mean the area was able to provide all resources required by the species, including food, shelter, mates, etc.
For example, for a small mammal, the edge effects associated with a narrow strip of suburban woodland nestled between two rows of residential blocks may prevent it being classified as suitable core habitat. For an aquatic species, a stream may need to be some minimum width to provide sufficient core habitat for the species to move around in. If a core habitat patch in this instance is considered to have a rectangular shape, what would be the minimum width of the shorter side, regardless of how long the longer side might be?
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 100 | 30 | 250 | Very hard to generalise | 60 | Small_medium_terrestrial_mammal | min_width_core | Initial |
| 40 | 1000 | 500 | 2000 | No direct experience with this one again. Thinking logically for the medium-sized macropods and that a patch would need to be a least 500m wide maybe. | 10 | Small_medium_terrestrial_mammal | min_width_core | Initial |
| 41 | 300 | 100 | 500 | Small mammals with small core ranges may survive in small 100m2 patches, but to sustain small mammal diversity would require larger patches. | 70 | Small_medium_terrestrial_mammal | min_width_core | Initial |
| 42 | 50 | 10 | 100 | Maclagan et al 2019 - life in linear for SBB. | 60 | Small_medium_terrestrial_mammal | min_width_core | Initial |
| 43 | 100 | 50 | 200 | Lost of native small mammals will require significant patch size/width to make habitat suitable | 25 | Small_medium_terrestrial_mammal | min_width_core | Initial |
| 45 | 1000 | 1000 | 1000 | not confident with this hence entering all the same numbers however I do think that 1000m is the lower | 0 | Small_medium_terrestrial_mammal | min_width_core | Initial |
| 47 | 50 | 10 | 100 | This will vary widely for the species, I’ve focused on small species like rodents | 50 | Small_medium_terrestrial_mammal | min_width_core | Initial |
| 48 | 2000 | 1000 | 3000 | Antechinus agilis, Antechinus flavipes, Bettongia gaimardi, Dasyurus maculatus, Dasyurus viverrinus, Perameles nasuta, Sminthopsus murina, Vombatus ursinus | 5 | Small_medium_terrestrial_mammal | min_width_core | Initial |
| 49 | 600 | 300 | 800 | My decision is based on working in the NSW and ACT region, where I observed that this taxon group were more commonly seen in core habitat with at least 300 m width. This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. This work hasn’t been published yet. | 60 | Small_medium_terrestrial_mammal | min_width_core | Initial |
| Aggregated | 578 | 333 | 883 | NA | 38 | Small_medium_terrestrial_mammal | min_width_core | Aggregated |
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This metric relates to the minimum dimensions of an area which could be considered suitable habitat for the taxon group to move through, e.g. between different patches of ‘core’ habitat, or when dispersing (e.g. as a sub-adult looking for a new home range). Corridor habitat would need to provide all resources required by the species to effectively move through the urban space, e.g. suitable perch sites for birds, suitable protection from predation for mammals and reptiles.
For example, for a small mammal, the edge effects associated with a narrow strip of suburban woodland nestled between two rows of residential blocks may prevent it being classified as suitable core habitat, but it might be sufficient habitat to facilitate movement through the area. For an aquatic species, a stream may need to be some minimum width to provide sufficient core habitat for the species to move around in, however the same species may be able to navigate a narrow culvert if just being used as part of a movement corridor. If a movement corridor in this instance is considered to have a rectangular shape, what would be the minimum width of the shorter side, regardless of how long the longer side might be?
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 50 | 10 | 100 | Providing there is sufficient ground-level cover, a corridor could be quite narrow but still functional | 75 | Small_medium_terrestrial_mammal | min_width_corridor | Initial |
| 40 | 100 | 80 | 150 | None | 10 | Small_medium_terrestrial_mammal | min_width_corridor | Initial |
| 41 | 3 | 2 | 5 | While these estimates may allow a species to move through the landscape, they will be at increased predation pressure, especially in the urban landscape (i.e. from outdoor cats). | 60 | Small_medium_terrestrial_mammal | min_width_corridor | Initial |
| 42 | 20 | 2 | 50 | Maclagan et al 2019 | 60 | Small_medium_terrestrial_mammal | min_width_corridor | Initial |
| 43 | 25 | 10 | 50 | A bit of a guess | 25 | Small_medium_terrestrial_mammal | min_width_corridor | Initial |
| 45 | 50 | 1 | 200 | based on the range of sizes. Not taking into account learnt predator behaviours in the corridor | 50 | Small_medium_terrestrial_mammal | min_width_corridor | Initial |
| 47 | 200 | 50 | 1000 | Here focused more on larger species and gliders that will rely on a decent corridor width | 50 | Small_medium_terrestrial_mammal | min_width_corridor | Initial |
| 48 | 25 | 5 | 30 | Antechinus agilis, Antechinus flavipes, Bettongia gaimardi, Dasyurus maculatus, Dasyurus viverrinus, Perameles nasuta, Sminthopsus murina, Vombatus ursinus | 10 | Small_medium_terrestrial_mammal | min_width_corridor | Initial |
| 49 | 300 | 50 | 500 | My decision is based on working in the NSW and ACT region, where I observed that this taxon group were more commonly seen in corridors with at least 50 m width (feral predators activities should be considered here for SMs). This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. This work hasn’t been published yet. | 60 | Small_medium_terrestrial_mammal | min_width_corridor | Initial |
| Aggregated | 86 | 23 | 232 | NA | 44 | Small_medium_terrestrial_mammal | min_width_corridor | Aggregated |
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This metric describes how far dispersing individuals from this taxon group will travel, usually to find a new home range or territory. This metric assumes the availability of continuous habitat.
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 500 | 50 | 5000 | Again, highly variable | 60 | Small_medium_terrestrial_mammal | disperal_distance | Initial |
| 40 | 0 | 0 | 0 |
Zeros presented for now as (1) no specific expertise, and (2) I think this Q would benefit from further clarification. When thinking “typical” for the group, are we wanting to capture the likely range for the component with the greatest distance requirements, or capture the range of the whole group where “low estimate” = species that barely need to disperse, “high estimate” = species that disperse massive distances? I assume the latter, but to answer this at all I would actually need to review the published literature |
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| 41 | 1000 | 100 | 4000 | Some species (especially male individuals) require large dispersal distances to access new gene pools away from their kin. | 60 | Small_medium_terrestrial_mammal | disperal_distance | Initial |
| 42 | 1500 | 100 | 15000 | average of bandicoots, quolls and smaller spp | 60 | Small_medium_terrestrial_mammal | disperal_distance | Initial |
| 43 | 500 | 100 | 5000 | I’ve radio tracked native and exotic small mammals and the sometimes (presumably when dispersing) disappear beyond telemetry range of small transmitters100-200m. Medium sized mammals, particularly predators can disperse 10’s of km’s | 25 | Small_medium_terrestrial_mammal | disperal_distance | Initial |
| 45 | 3000 | 200 | 5000 | Dependant on the species | 50 | Small_medium_terrestrial_mammal | disperal_distance | Initial |
| 47 | 200 | 0 | 1000 | depends on size of animal and density at natal site | 50 | Small_medium_terrestrial_mammal | disperal_distance | Initial |
| 48 | 500 | 200 | 800 | Antechinus agilis, Antechinus flavipes, Bettongia gaimardi, Dasyurus maculatus, Dasyurus viverrinus, Perameles nasuta, Sminthopsus murina, Vombatus ursinus | 10 | Small_medium_terrestrial_mammal | disperal_distance | Initial |
| 49 | 500 | 10 | 1000 | My decision is based on working in the NSW and ACT region, where I observed that this taxon group were more commonly seen in connected habitats about 100 m apart from each other. Living trapping in the future may help to answer this question. This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. This work hasn’t been published yet. | 40 | Small_medium_terrestrial_mammal | disperal_distance | Initial |
| Aggregated | 856 | 84 | 4089 | NA | 39 | Small_medium_terrestrial_mammal | disperal_distance | Aggregated |
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This metric describes how far an individual typically moves within a suitable habitat patch. It could be considered as the distance between the centre and the edge of a home range or territory.
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 500 | 50 | 1000 | Highly variable | 60 | Small_medium_terrestrial_mammal | movement_within | Initial |
| 40 | 1000 | 100 | 10000 | Small species can have small ranges, etc. | 20 | Small_medium_terrestrial_mammal | movement_within | Initial |
| 41 | 1000 | 50 | 1500 | For small mammals (excluding flying-foxes and other outliers) core ranges are usually a few kilometres. | 80 | Small_medium_terrestrial_mammal | movement_within | Initial |
| 42 | 600 | 100 | 5000 | average of spp with larger HR (e.g. STQ) and those wtih smaller HR | 60 | Small_medium_terrestrial_mammal | movement_within | Initial |
| 43 | 200 | 100 | 1000 | Guessing again | 10 | Small_medium_terrestrial_mammal | movement_within | Initial |
| 45 | 2000 | 100 | 5000 | This would change depending on food and shelter availability | 50 | Small_medium_terrestrial_mammal | movement_within | Initial |
| 47 | 100 | 0 | 1000 | Again depends on population density, also on trophic role of the animal. Carnivores will move further than herbivores. estimates have been based on small mammals like rodents and antechinus | 50 | Small_medium_terrestrial_mammal | movement_within | Initial |
| 48 | 200 | 100 | 2000 | Antechinus agilis 20, Antechinus flavipes 20, Bettongia gaimardi 200, Dasyurus maculatus 2000, Dasyurus viverrinus 500, Perameles nasuta 200, Sminthopsus murina 20, Vombatus ursinus 3000 | 10 | Small_medium_terrestrial_mammal | movement_within | Initial |
| 49 | 100 | 10 | 200 | My decision is based on working in the NSW and ACT region such as the live trapping in NSW in 2018. This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. This work hasn’t been published yet. | 50 | Small_medium_terrestrial_mammal | movement_within | Initial |
| Aggregated | 633 | 68 | 2967 | NA | 43 | Small_medium_terrestrial_mammal | movement_within | Aggregated |
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This metric aims to quantify how far this taxon group can or will typically move outside of areas mapped as suitable habitat. For example, a kangaroo might be able to cross a road, even though a road is not classified as suitable habitat, so long as there are no wildlife exclusion fences. A cockatoo might be able to move across a suburb between one suitable woodland habitat patch and another.
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 100 | 50 | 500 | It’s very contingent on how ‘hostile’ the matrix is and again what species you’re considering | 60 | Small_medium_terrestrial_mammal | capacity_movement | Initial |
| 40 | 100 | 5 | 500 | Some small mammals will not tolerate more than a few metres (low), while medium-sized macropods would probably tolerate a few hundred (high). Maybe | 20 | Small_medium_terrestrial_mammal | capacity_movement | Initial |
| 41 | 20 | 10 | 30 | Some small mammals may be able to cross a road to enter another patch of habitat. | 70 | Small_medium_terrestrial_mammal | capacity_movement | Initial |
| 42 | 10 | 5 | 500 | Maclagan et al 2019 | 60 | Small_medium_terrestrial_mammal | capacity_movement | Initial |
| 43 | 0 | 0 | 0 | Highly variable between species | 0 | Small_medium_terrestrial_mammal | capacity_movement | Initial |
| 45 | 40 | 10 | 100 | This would depend on predators in the area, the more comfortable the animals are the further they go | 40 | Small_medium_terrestrial_mammal | capacity_movement | Initial |
| 47 | 20 | 0 | 100 | based on smaller mammal species | 50 | Small_medium_terrestrial_mammal | capacity_movement | Initial |
| 48 | 50 | 5 | 100 | Antechinus agilis, Antechinus flavipes, Bettongia gaimardi, Dasyurus maculatus, Dasyurus viverrinus, Perameles nasuta, Sminthopsus murina, Vombatus ursinus | 5 | Small_medium_terrestrial_mammal | capacity_movement | Initial |
| 49 | 30 | 10 | 50 | My decision is based on working in the NSW and ACT region such as the live trapping in NSW in 2018 and camera trapping in 2021. This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. This work hasn’t been published yet. | 50 | Small_medium_terrestrial_mammal | capacity_movement | Initial |
| Aggregated | 41 | 11 | 209 | NA | 39 | Small_medium_terrestrial_mammal | capacity_movement | Aggregated |
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The next series of visualisations relate to barriers to movement.
This is the final section of this survey. This section asks questions regarding barriers to movement in the urban space, which might be represented by vertical barriers (fences, walls, buildings, gutters), water barriers (lakes, streams, rivers), substrate barriers (e.g. concrete or bitumen) or barriers relating to the use of an area by people (traffic, pedestrians). By quantifying these barriers we can use remote sensing data to identify their location in the urban environment and demonstrate functional habitat fragmentation.
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This metric aims to capture the distance this taxon group can move across a paved surface, e.g. concrete or bitumen. Examples might include bike or pedestrian paths, roads and driveways, concrete drainage channels, tennis courts, car parks, etc. For reptiles, for example, a taxon group may choose this substrate as a basking site but not be able to move a long distance due to the lack of suitable habitat cover to protect from predation. For fish, platypus or turtles, there may be some maximum distance a species can move through an artificial waterbody (e.g. a concrete drainage channel) between naturalised pools or streams.
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 50 | 10 | 100 | Most small and medium-sized mammals really don’t like crossing paved surfaces | 60 | Small_medium_terrestrial_mammal | paved_surface | Initial |
| 40 | 50 | 40 | 100 | NA | 20 | Small_medium_terrestrial_mammal | paved_surface | Initial |
| 41 | 20 | 10 | 30 | Some small mammals may be able to cross a road to enter another patch of habitat. | 70 | Small_medium_terrestrial_mammal | paved_surface | Initial |
| 42 | 5 | 2 | 30 | Maclagan et al 2019 | 60 | Small_medium_terrestrial_mammal | paved_surface | Initial |
| 43 | 0 | 0 | 0 | Highly variable between species | 0 | Small_medium_terrestrial_mammal | paved_surface | Initial |
| 45 | 20 | 2 | 50 | This answer is based on predation risk | 50 | Small_medium_terrestrial_mammal | paved_surface | Initial |
| 47 | 10 | 0 | 50 | Depends greatly on body size | 60 | Small_medium_terrestrial_mammal | paved_surface | Initial |
| 48 | 10 | 4 | 30 |
Antechinus agilis, Antechinus flavipes, Bettongia gaimardi, Dasyurus maculatus, Dasyurus viverrinus, Perameles nasuta, Sminthopsus murina, Vombatus ursinus Thinking mainly of Antechinus and Sminthopsus |
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| 49 | 30 | 25 | 50 | My decision is based on working in the NSW and ACT region such as the live trapping in NSW in 2018 and camera trapping in 2021. This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. This work hasn’t been published yet. | 55 | Small_medium_terrestrial_mammal | paved_surface | Initial |
| Aggregated | 22 | 10 | 49 | NA | 42 | Small_medium_terrestrial_mammal | paved_surface | Aggregated |
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This metric aims to determine how much of a vertical structure will impede movement by this taxon group. For example, turtles may not be able to climb up a steep roadside curb, however for a gecko a vertical structure equivalent to a multi-storey building may not be prevent movement. Birds may be able to cross vertical barriers of any height, unless they are flightless.
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 3.0 | 1.0 | 10.0 | So species-dependent, some are excelllent climbers, others are not, it will also depend on the nature of barrier (is it solid or can it be easily climbed?) | 60 | Small_medium_terrestrial_mammal | max_height_building | Initial |
| 40 | 0.6 | 0.5 | 0.7 | Small mammal enclosures at Mulligans are approximately 1m tall. | 80 | Small_medium_terrestrial_mammal | max_height_building | Initial |
| 41 | 5.0 | 2.0 | 30.0 | Some small mammals will be very constrained by vertical barriers (e.g. ground dwellers like native rodents, dasyurids). | 70 | Small_medium_terrestrial_mammal | max_height_building | Initial |
| 42 | 15.0 | 10.0 | 30.0 | based on spp size (taking into account range of spp sizes) | 60 | Small_medium_terrestrial_mammal | max_height_building | Initial |
| 43 | 0.0 | 0.0 | 0.0 | I don’t know | 0 | Small_medium_terrestrial_mammal | max_height_building | Initial |
| 45 | 2.0 | 0.5 | 10.0 | this is based on some animals being arboreal and some ground dwelling. I believe the arboreal animals could get higher but based results on average | 50 | Small_medium_terrestrial_mammal | max_height_building | Initial |
| 47 | 1.0 | 0.0 | 5.0 | Echidna is the exception to this from the list of ACT mammals I can think of. I’d lower the values for that species | 50 | Small_medium_terrestrial_mammal | max_height_building | Initial |
| 48 | 1.2 | 1.0 | 2.0 |
Antechinus agilis, Antechinus flavipes, Bettongia gaimardi, Dasyurus maculatus, Dasyurus viverrinus, Perameles nasuta, Sminthopsus murina, Vombatus ursinus Bettongs and bandicoots are easily stopped by solid barriers |
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| 49 | 0.5 | 0.0 | 0.7 | My decision is based on working in the NSW and ACT region such as the live trapping in NSW in 2018 and camera trapping in 2021. This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. They can climb up to 4-5 m but may not be able to move bewteen trees. | 50 | Small_medium_terrestrial_mammal | max_height_building | Initial |
| Aggregated | 3.1 | 1.7 | 9.8 | NA | 48 | Small_medium_terrestrial_mammal | max_height_building | Aggregated |
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This metric aims to quantify the size of a gap which would allow passage of this taxon group through what would otherwise be a barrier (e.g. a fence, or a culvert). For example, an antechinus might be able to pass through a chain link fence, however a turtle may not.
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 0.50 | 0.15 | 1.00 | Species dependent | 60 | Small_medium_terrestrial_mammal | gap_dimensions | Initial |
| 40 | 1.00 | 0.50 | 2.00 | Whatever size wire fencing wont exclude a wallaby? | 50 | Small_medium_terrestrial_mammal | gap_dimensions | Initial |
| 41 | 0.20 | 0.05 | 0.30 | Depends on the size of the small mammal, but based on brushtail possums which can squeeze through spaces as small as 20 cm across, 20cm would be best to allow for dispersal through these barriers. | 75 | Small_medium_terrestrial_mammal | gap_dimensions | Initial |
| 42 | 20.00 | 5.00 | 40.00 | based on spp size (taking into account range of spp sizes) | 60 | Small_medium_terrestrial_mammal | gap_dimensions | Initial |
| 43 | 0.50 | 0.25 | 1.00 | Depends on if the gap is near some structure/refuge area | 5 | Small_medium_terrestrial_mammal | gap_dimensions | Initial |
| 45 | 0.01 | 0.00 | 0.02 | based on average size | 50 | Small_medium_terrestrial_mammal | gap_dimensions | Initial |
| 47 | 1.00 | 0.10 | 5.00 | This is something that will of course vary greatly with body size | 50 | Small_medium_terrestrial_mammal | gap_dimensions | Initial |
| 48 | 0.50 | 0.25 | 1.00 | Antechinus agilis 0.02, Antechinus flavipes 0.02, Bettongia gaimardi 0.25, Dasyurus maculatus, Dasyurus viverrinus, Perameles nasuta 0.1, Sminthopsus murina 0.02, Vombatus ursinus 0.5 | 50 | Small_medium_terrestrial_mammal | gap_dimensions | Initial |
| 49 | 0.70 | 0.70 | 5.00 | My decision is based on working in the NSW and ACT region such as the live trapping in NSW in 2018 and camera trapping in 2021. This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. They can climb up to 4-5 m but may not be able to move bewteen trees. | 50 | Small_medium_terrestrial_mammal | gap_dimensions | Initial |
| Aggregated | 2.71 | 0.78 | 6.15 | NA | 50 | Small_medium_terrestrial_mammal | gap_dimensions | Aggregated |
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This metric aims to quantify the distance this taxon group can move across a permanent waterbody. In some instances, larger species such as kangaroos may be readily able to navigate a small stream by hopping from one side to the other, however the same might not be possible for a small grassland reptile.
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 50 | 5.0 | 100 | Again, species dependent | 50 | Small_medium_terrestrial_mammal | max_waterbody | Initial |
| 40 | 1 | 0.0 | 5 | NA | 20 | Small_medium_terrestrial_mammal | max_waterbody | Initial |
| 41 | 30 | 5.0 | 50 | It is difficult to know how far some small mammals can swim, but given enough pressure, I would posit that most could swim across 30m of open water. | 50 | Small_medium_terrestrial_mammal | max_waterbody | Initial |
| 42 | 20 | 15.0 | 50 | based on range of spp abilities | 60 | Small_medium_terrestrial_mammal | max_waterbody | Initial |
| 43 | 0 | 0.0 | 0 | No idea | 0 | Small_medium_terrestrial_mammal | max_waterbody | Initial |
| 45 | 7 | 1.0 | 20 | For the smaller species I would have liked to go lower | 50 | Small_medium_terrestrial_mammal | max_waterbody | Initial |
| 47 | 2 | 0.0 | 10 | tried to balance well across smaller and larger species of this group | 50 | Small_medium_terrestrial_mammal | max_waterbody | Initial |
| 48 | 2 | 1.0 | 10 |
Antechinus agilis, Antechinus flavipes, Bettongia gaimardi, Dasyurus maculatus, Dasyurus viverrinus, Perameles nasuta, Sminthopsus murina, Vombatus ursinus thinking mainly Antechinus |
20 | Small_medium_terrestrial_mammal | max_waterbody | Initial |
| 49 | 1 | 1.0 | 3 | My decision is based on working in the NSW and ACT region such as the live trapping in NSW in 2018 and camera trapping in 2021 with creeks and small rivers. This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. | 50 | Small_medium_terrestrial_mammal | max_waterbody | Initial |
| Aggregated | 13 | 3.1 | 28 | NA | 39 | Small_medium_terrestrial_mammal | max_waterbody | Aggregated |
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This metric aims to quantify the level of vehicle traffic (including boats in an urban waterbody) which would represent a barrier to this taxon group. The number should be based on the amount of traffic occurring during the species’ active part of the day or night. For example, an echidna may be willing and able to cross a road at night when there is little traffic, however during the day an increased traffic volume may result in the road (or rather, the traffic on the road) becoming a barrier for this species. A similar approach can be applied to aquatic and riparian species in terms of boat traffic.
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 12.0 | 10.0 | 30 | Depends on type of road and habitat | 50 | Small_medium_terrestrial_mammal | traffic_flow | Initial |
| 40 | 0.0 | 0.0 | 0 | Difficult to say, given driver behaviour and type of traffic (major roads, speed) would be critically important to any estimate. Maybe not important as a metric? | 0 | Small_medium_terrestrial_mammal | traffic_flow | Initial |
| 41 | 6.0 | 3.0 | 12 | Small mammals will be deterred and endangered by constant vehicle traffic. Most species should be able to cross roads with one vehicle passing every 10 m. | 60 | Small_medium_terrestrial_mammal | traffic_flow | Initial |
| 42 | 5.0 | 0.0 | 10 | based on observations of animals next to road (e.g. wombats) | 60 | Small_medium_terrestrial_mammal | traffic_flow | Initial |
| 43 | 0.0 | 0.0 | 0 | No idea | 0 | Small_medium_terrestrial_mammal | traffic_flow | Initial |
| 45 | 1.0 | 0.0 | 1 | I have no confidence in my ability to answer this per hour | 0 | Small_medium_terrestrial_mammal | traffic_flow | Initial |
| 47 | 3.0 | 0.0 | 10 | again tried to balance across the range of mammals | 50 | Small_medium_terrestrial_mammal | traffic_flow | Initial |
| 48 | 10.0 | 6.0 | 120 | Antechinus agilis, Antechinus flavipes, Bettongia gaimardi, Dasyurus maculatus, Dasyurus viverrinus, Perameles nasuta, Sminthopsus murina, Vombatus ursinus | 5 | Small_medium_terrestrial_mammal | traffic_flow | Initial |
| 49 | 10.0 | 0.0 | 20 | My decision is based on working in the NSW and ACT region such as the live trapping in NSW in 2018 and camera trapping in 2021 in urban reserves. This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. | 40 | Small_medium_terrestrial_mammal | traffic_flow | Initial |
| Aggregated | 5.2 | 2.1 | 23 | NA | 29 | Small_medium_terrestrial_mammal | traffic_flow | Aggregated |
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This metric aims to quantify the level of pedestrian traffic (including swimmers in an urban waterbody) which would represent a barrier to this taxon group.The number should be based on the amount of pedestrians passing during the species’ active part of the day or night. A similar approach can be applied to aquatic and riparian species in terms of people swimming in a waterbody.
For example, a kangaroo may be willing and able to cross school playground at dusk in summer when there are few people about, however during winter an increased use of the school oval for organised sports in the evening may result in the grassy area becoming a barrier for this species.
| Expert | Best | Lower | Upper | Comments | Confidence | Taxon | Variable | Group2 |
|---|---|---|---|---|---|---|---|---|
| 34 | 5 | 2.0 | 20 | Depends on surrounding habitat, species and degree of habituation to people | 50 | Small_medium_terrestrial_mammal | pedestrian_flow | Initial |
| 40 | 0 | 0.0 | 0 | Unaware of any research on this. Like the traffic, it would also be dependent on activity and other properties of the behaviour. Maybe. I dunno. :) | 0 | Small_medium_terrestrial_mammal | pedestrian_flow | Initial |
| 41 | 6 | 3.0 | 24 | For nocturnal small mammals, pedestrians could provide a similar barrier to their movement as would vehicular traffic. Again, one pedestrian passing every 10m would be ideal. | 60 | Small_medium_terrestrial_mammal | pedestrian_flow | Initial |
| 42 | 30 | 10.0 | 100 | based on general observaitons | 60 | Small_medium_terrestrial_mammal | pedestrian_flow | Initial |
| 43 | 0 | 0.0 | 0 | No idea | 0 | Small_medium_terrestrial_mammal | pedestrian_flow | Initial |
| 45 | 20 | 10.0 | 100 | This could be a lot of disturbance however depends on how the species can cope and how used to people they are. | 25 | Small_medium_terrestrial_mammal | pedestrian_flow | Initial |
| 47 | 10 | 0.0 | 20 | I don’t think pedestrians will be a major issue for most mammals | 50 | Small_medium_terrestrial_mammal | pedestrian_flow | Initial |
| 48 | 10 | 6.0 | 120 | Antechinus agilis, Antechinus flavipes, Bettongia gaimardi, Dasyurus maculatus, Dasyurus viverrinus, Perameles nasuta, Sminthopsus murina, Vombatus ursinus | 5 | Small_medium_terrestrial_mammal | pedestrian_flow | Initial |
| 49 | 10 | 10.0 | 20 | My decision is based on working in the NSW and ACT region such as the live trapping in NSW in 2018 and camera trapping in 2021 in urban reserves. This estimate is predominantly based on working with Agile Antechinus, CommonDunnart, and Yellow-footed Antechinus within the taxon group. | 40 | Small_medium_terrestrial_mammal | pedestrian_flow | Initial |
| Aggregated | 10 | 4.6 | 45 | NA | 32 | Small_medium_terrestrial_mammal | pedestrian_flow | Aggregated |