diff --git a/vocab_files/methods_by_module/signs-based-fauna/collection.ttl b/vocab_files/methods_by_module/signs-based-fauna/collection.ttl
index 7d27ceab7..35c46339e 100644
--- a/vocab_files/methods_by_module/signs-based-fauna/collection.ttl
+++ b/vocab_files/methods_by_module/signs-based-fauna/collection.ttl
@@ -12,96 +12,101 @@ PREFIX xsd: The Sign-based Fauna Survey Module covers the procedures and
guidelines of five protocols for recording the signs of fauna present in
a project area: The module is appropriate for monitoring all fauna species. However,
the methods outlined have been predominantly used to monitor pest fauna
species, which form the basis of the literature referenced and examples
provided. Depending on the project aims and environment, sign-based
-surveys can consist of a single protocol or a combination of the five
-protocols. Where possible, sign-based surveys are recommended to be
-undertaken within or near an established 1 ha Core Monitoring Plot or
-Fauna Plot so that the data to be analysed in combination with
-vegetation and landform data collected. The Within-plot belt transect protocol is
-implemented within the 1 ha plot at 1, 2, 3 or 4 100 m transects
+surveys can consist of a single protocol or a combination of protocols.
+Where possible, sign-based surveys are recommended to be undertaken
+within or near an established 1 ha Core Monitoring Plot or Fauna Plot to
+enable the data to be analysed in combination with vegetation and
+landform data.Contents
-Module overview
-Available protocols
+Module Overview
+Available Protocols
-
The Off-plot belt transect protocol is conducted -outside any established plot within the project area. The surveyor can -set the length of off-plot belt transects ranging from 100 m to 5 km. -Similarly, the surveyor can set the length and width of each consecutive -quadrats. Quadrats can be 1 m x 1 m (recommended for densely vegetated -areas or areas with lots of animal activity) and up to 4 m x 20 m -(recommended for more sparsely vegetated communities).
-Plot sign search protocol involves recording the -presence and age of signs of any fauna observed across the plot (either -2 ha if in arid systems or 1 ha if elsewhere). If a vehicle track is -nearby, an additional 100 m track survey can also be conducted to -supplement the presence records. The active plot sign search protocol is -best suited to sandy environments (either arid or coastal systems) where -tracks can be readily left by animals and where the substrate is not -heavily vegetated or covered in leaf litter to impede tracks being left. -Note this protocol is similar to the Active search protocol of the -Vertebrate Fauna Module, however in this module the focus is on looking -for signs of fauna presence, whilst the Active search protocol allows -for disturbance techniques for searching for fauna present.
-Vehicle track protocol can be undertaken along -a continuous transect which usually comprises a dirt road or vehicle +presence of each sign type along with the attributed species is +recorded, or the absence of signs (minimum data requirement). In +addition, the protocol can be implemented in succession with the +Herbivory and Physical Damage Module, whereby the extent of physical +damage or herbivory is recorded in the same quadrats.
+The Off-plot Belt Transect Protocol is conducted +outside any established plot within the project area. The length of +off-plot belt transects can be set, with a minimum of 100 m. Similarly, +the length and width of the consecutive quadrats can be set. Quadrats +can be 1 m x 1 m (recommended for densely vegetated areas or areas with +lots of animal activity) and up to 4 m x 20 m (recommended for more +sparsely vegetated communities).
+The Plot Sign Search Protocol involves recording the +presence and age of signs of fauna observed across the Core Monitoring +Plot, Fauna Plot or Biodiversity Plot (a 2 ha search area in arid +systems is recommended). If a vehicle track is nearby (within 200 m), an +additional 100 m track survey can also be conducted to supplement the +presence records. The optional track survey is best suited to +environments where the substrate is conducive to animal tracks +imprinting and heavy vegetation or leaf litter do not impede tracks +being left (e.g. open, sandy arid environments). Note this protocol is +similar to the Active search protocol of the Vertebrate Fauna Module, +however in this module the focus is on looking for signs of fauna +presence, whilst the Active search protocol allows for disturbance +techniques for searching for fauna present.
+The Vehicle Track Protocol can be undertaken along a +continuous transect which usually comprises a dirt road or vehicle track. Dirt roads and vehicle tracks are prepared using a heavy object towed behind a vehicle and revisited on subsequent days to record the -tracks present. Typically track plots are established at set distance +tracks present. Typically, track plots are established at set distance intervals reflecting the target species' home range while ensuring -independence.
-Track stations protocol can be undertaken within -defined track plots such as sand pads. The track plots are often +independence. The Vehicle track protocol is best suited to environments +where the substrate is conducive to animal tracks imprinting (e.g. sandy +arid environments).
+The Track Stations Protocol can be undertaken within +defined track stations such as sand pads. The track stations are often prepared and cleared using a broom and revisited on subsequent days to -record the tracks present. Typically track plots are established at set -distance intervals reflecting the target species' home range while -ensuring independence.
+record the animal tracks present. Typically track stations are +established at set distance intervals reflecting the target species' +home range while ensuring independence. The Track stations protocol is +best suited to environments where the substrate is conducive to animal +tracks imprinting (e.g., sandy arid environments). However, sand or +another suitable tracking substrate can be installed at track stations +to complete the survey.Mandatory if the Within-plot belt transect and Plot sign search protocols are used:
Plot Selection and Layout Module – within-plot 100 m belt -transects and plot sign searches can be undertaken within Core +
Plot Selection and Layout Module – within-plot 100 m belt +transects, and plot sign searches can be undertaken within Core Monitoring Plots or Fauna Plots. Therefore, ensure that the Plot -Selection and Layout Module has been completed before -commencing.
Herbivory and Physical Damage Module – both modules can be -implemented in unison, whereby signs of fauna and the extent of physical -damage or herbivory is recorded within plots (belt transects, entire -plot or subset area) or off-plot belt transects.
Vertebrate Fauna Module – sign-based fauna data can inform localities to establish Fauna Plots and contribute to overall monitoring data of vertebrate fauna species within a project area.
Higashide, D., T. Kuriyama, S. Takagi, Y. Nakashima, K. Fukasawa, G. Yajima, M. Kasada, and M. Yokoyama. 2021. Effectiveness of signs of @@ -175,9 +180,6 @@ Energy. Department of the Environment and Energy, Canberra.
Kennedy, M., B. L. Phillips, S. Legge, S. A. Murphy, and R. A. Faulkner. 2012. Do dingoes suppress the activity of feral cats in northern Australia? Austral Ecology 37:134-139.
-Koichi, K., D. Holliday, and C. e. Harris. 2020. Glovebox Guide for -Managing Feral Pigs v2.0. PestSmart Toolkit publication., The Centre for -Invasive Species Solutions, Canberra ACT.
Masters, P., N. Markopoulos, B. Florance, and R. Southgate. 2018. The eradication of fallow deer (Dama dama) and feral goats (Capra hircus) from Kangaroo Island, South Australia. @@ -226,7 +228,7 @@ Network at WWF Australia, Sydney.
Backhouse, K. Bellchambers, R. Brandle, P. Brenton, and P. Copley. 2022. Designing a large‐scale track‐based monitoring program to detect changes in species distributions in arid Australia. Ecological -Applications:e2762. +applications:e2762.Threatened Species Recovery Hub. undated. Data collection in track-based surveys.
Triggs, B. 1996. Tracks, scats and other traces. A field guide to @@ -235,13 +237,10 @@ Australian mammals. Oxford University Press Australia, Melbourne.
estimate the abundance of terrestrial carnivores using field signs and observation. Wildlife Research 28:151-164."""^^rdf:HTML ; rdfs:isDefinedByTable 1. Key -definitions and terms used in the Sign-based Fauna Survey Module.
-AZM | +Arid Zone Monitoring | +|
Bait | Edible attractant such as meat or oats, that in some instances is poisoned. | |
Bait-station | Consists of a mounted lure used in association with a track plot to increase the probability of detecting a target species or a suite of species. Food lures usually protected from consumption or removal in a secure container that allows airflow. | |
Belt-transect | Method of sampling a survey area whereby a transect is placed and a set area either side of the transect is inspected for signs. | |
Buck-heap | Accumulation of rabbit pellets in a latrine. Recorded as a buck heap when the number of individual pellets exceeds 40. | |
Decay rate | The time taken for scats to decompose, influenced by factors such as termites, rainfall, substrate and season. | |
EPBC Act | Environment Protection and Biodiversity Conservation Act 1999 | |
Faecal accumulation rate (FAR) | The density of scats that have accumulated in a survey quadrat over a specified period of time after the survey quadrat was previously cleared of all scats. | |
Fixed interval plot | Survey design where plots are located at a predefined distance from -one another | +one another.|
Sand drag | A bar or chain is towed behind a 4WD vehicle to clear the substrate -of tracks to enable a clean surface to detect subsequent presence of -fauna species | +of animal tracks to enable a clean surface to detect subsequent presence +of fauna species.|
Segment | A segment refers to a section within the transect, and typically relates to a survey tape length. | |
Lure | Attractant used to encourage a target species or a suite of species to investigate a specific point. Can be olfactory, auditory, visual or some combination of these in nature. | |
Plot | The specific survey area where information is collected (generally -100 m x 100 m; 1 ha). Final plot location is determined in the field, -with preference given to homogeneous areas representative of the broader +100 x 100 m; 1 ha). Final plot location is determined in the field, with +preference given to homogeneous areas representative of the broader project area, with a constant mix of vegetation, relief and soil. | |
Track count | -Track count survey that occurs on a pre-existing track or road | +Track count survey that occurs on a pre-existing track or road. |
Sand plot | Plot used to record footprints where external medium (sand) is added -to the area | +to the area.|
Sign | -Any general evidence indicating an animal’s presence in an -area. -Common signs of the target pest fauna include tracks, scats, dens and -burrows, skeletal remains, scratch marks, hair, evidence of predation, -and physical damage to the environment caused by browsing, rubbing, -trampling, rooting, digging and wallowing. |
+Any general evidence indicating an animal’s presence in an area. +Common signs include tracks, scats, dens and burrows, skeletal remains, +scratch marks, hair, evidence of predation, and physical damage to the +environment caused by browsing, rubbing, trampling, rooting, digging and +wallowing. |
Scat | Faeces/faecal pellets/dung/droppings of animals. Often individual or -scattered pellets (e.g. rabbit), or clumped pellet groups (e.g. deer). +scattered pellets (e.g., rabbit), or clumped pellet groups (e.g. deer). Their deposition will be influenced by diet (wet diet often causes clumping of pellets) and their size can reflect age (adult/juvenile). Scat surveys provide an estimate of relative abundances suitable for both herbivores and predators. | |
Track | Imprint left by an animal on the ground surface, with variables including shape, width, length and stride used to identify species (Moseby et al. 2009). Track surveys provide an estimate of relative abundances suitable for both herbivores and predators. | |
Track station | -Small area (usually 1 m2) used to record footprints | +Small area (usually 1 m2) used to animal tracks. |
Transect | A line placed across an area that is traversed by the surveyor to -record observations or take measurements | +record observations or take measurements.|
Trimble® R1 | A rugged, compact, lightweight Global Navigation Satellite System (GNSS) receiver (configured with the GNSS Status app) that provides @@ -368,190 +370,6 @@ professional-grade positioning information to any connected mobile device using Bluetooth® connectivity. |
Key information available from sign-based surveys of pest species -that should be considered during the survey design stage is included in -Table 2.
-Table 2. Recommended -survey designs for pest fauna species.
-Pest fauna | -Recommended approach | -Transect length and width | -Active period | -Other comments / considerations | -Key resources | -
---|---|---|---|---|---|
Feral cat | -Continuous transect/track plots along a transect | -
- Plots minimum of 1 m in width -Transect minimum of 10 km in length - |
-
- Predominantly nocturnal. -Greatest periods of activity during dusk and dawn. - |
-
- Track plots should be 3 cm deep -Survey should be conducted for three consecutive nights - |
-
- Monitoring Techniques for Vertebrate Pests: Feral Cats (Mitchell and -Balogh 2007b) -A guide to surveying red foxes and feral cats in Australia (Hradsky -et al. 2021) - |
-
Fox | -Continuous transect/track plots along a transect | -
- Minimum of 26 stations at 1 km intervals along a transect -Continuous transect 10 km in length - |
-
- Predominantly nocturnal. -Most active from dusk until dawn. - |
-
- Track plots should be 3 cm deep -Survey should be conducted for three consecutive nights - |
-
- Monitoring Techniques for Vertebrate Pests: Foxes (Mitchell and -Balogh 2007e) -A guide to surveying red foxes and feral cats in Australia (Hradsky -et al. 2021) - |
-
Wild dog | -Continuous transect/track plots along a transect | -
- Minimum of 26 stations at 1 km intervals along a transect -Continuous transect 10 km in length and 2-3 m in width - |
-
- Predominantly nocturnal. -Greatest periods of activity during dusk and dawn. - |
-
- Survey should be conducted for three consecutive nights -Track plots should be 3 cm deep - |
-
- Monitoring Techniques for Vertebrate Pests: Wild Dogs (Mitchell and -Balogh 2007f) - |
-
Rabbit | -Belt transect/continuous transect | -
- Minimum 200 m transect -Belt minimum of 2 m in width -10 m width recommended if warrens being included in the survey -Continuous transects should be a minimum of 50 m - |
-
- Predominantly nocturnal. -Active from dusk until dawn. -Greatest periods of activity during dusk and dawn. - |
-
- 2 ha active search within a plot also effective for rabbit signs -Survey should be conducted for three consecutive nights -Substrate should be 1-3 cm deep - |
-
- Monitoring Techniques for Vertebrate Pests: Rabbits(Mitchell and -Balogh 2007a) -Best Practice Management Guide for Rabbits in the ACT (ACT Government -2015) - |
-
Feral deer | -Circular plots along a transect/belt transect | -
- Minimum of 500 m in length -Minimum of 0.5 m belt size -Transects split into 50 m segments - |
-
- Activity depends on deer species: -Sambar peak near sunset. -Red deer peak at dawn and dusk. -Fallow peak at dusk and dawn. - |
-
- Thin narrow plots also useful because they are simple to set up and -are rapid to complete - |
-
- Ecological Deer Management Manual (Moriarty and Brown 2012) - |
-
Feral goat | -2 ha active search/belt transect | -
- 150 m transects -1 m belt width or plot radius along the transect - |
-
- Predominantly diurnal. -Peak activity in early morning and late afternoon. - |
-
- Area should be cleared and resurveyed at 2 month intervals -When plots along a transect used they should be spaced at 3 m -intervals - |
-
- Monitoring Techniques for Vertebrate Pests: Feral Goats (Mitchell and -Balogh 2007c) - |
-
Feral pig | -Track plots along a transect | -
- 1 m wide plots -Plots each 200 m – 1 km along the transect -Transects should be greater than 1 km - |
-
- Peak activity in early morning and late afternoon (Koichi et al. -2020). - |
-
- Survey should be conducted for three consecutive nights -There should be 78 plot nights completed -Substrate should be 3 cm deep - |
-
- Monitoring Techniques for Vertebrate Pests: Feral Pigs (Mitchell and -Balogh 2007d) - |
-
Appendix 1. Data -collection fields from the Signs-based Fauna Survey Module
Complete lists are provided in the Monitor app, as well as the TERN -website
+website.Transect route type | +Route type |
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Survey intent | +Survey intent |
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Target species | +Target species |
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Survey type | +Tracking substrate |
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Observer role | +Track station substrate |
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Weather conditions | +Habitat (Major Vegetation Group) |
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Sign type* (not a complete list) | +Weather conditions |
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NVIS Major Vegetation Group | -NVIS Major Vegetation Sub-group | -|
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Rainforest and Vine Thickets (MVG 1) | -Cool temperate rainforest | +
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Tropical or sub-tropical rainforests | +
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Dry rainforest | +
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Vine thickets | +
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Eucalypt Tall Open Forests (MVG 2) | -Eucalyptus tall open forests with a dense broad-leaved and/or -tree-fern understorey (wet-sclerophyll) | +
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Eucalyptus tall open forests with a fine-leaved shrubby understorey -OR Eucalyptus tall open forests and open forests with ferns, herbs, -sedges, rushes or wet tussock grasses | +
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Eucalypt Open Forests (MVG 3) | -Eucalyptus open forests with a shrubby understorey | +
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Eucalyptus open forests with a grassy understorey | +
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Eucalypt Low Open Forests (MVG 4) | -- | +
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Eucalypt Woodlands (MVG 5) | -Eucalyptus woodlands with a shrubby understorey OR Eucalyptus -woodlands with a chenopod or samphire understorey | +
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Eucalyptus woodlands with a grassy understorey OR Eucalyptus -woodlands with ferns, herbs, sedges, rushes or wet tussock grassland OR -Eucalyptus woodlands with a hummock grass understorey | +
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Acacia Forests and Woodlands (MVG 6) | -Brigalow (Acacia harpophylla) forests and woodlands | +
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Other Acacia forests and woodlands | +
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Mulga (Acacia aneura) woodlands and shrublands +/- tussock -grass +/- forbs OR Mulga (Acacia aneura) woodlands and -shrublands with hummock grass | +
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Callitris Forests and Woodlands (MVG 7) | -Callitris forests and woodlands (Eastern occurrence) | +
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Callitris forests and woodlands (mallee, arid and semi-arid -occurrence) | +
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Casuarina Forests and Woodlands (MVG 8) | -Casuarina and Allocasuarina forests and woodlands | +
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River Oak forests and woodlands | +
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Melaleuca Forests and Woodlands (MVG 9) | -Melaleuca open forests and woodlands | +
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Other Forests and Woodlands (MVG 10) | -Other forests and woodlands OR Banksia woodlands OR Leptospermum -forests and woodlands OR Tropical mixed species forests and -woodlands | +
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Eucalypt Open Woodlands (MVG 11) | -Eucalyptus open woodlands with a grassy understorey OR Eucalyptus -open woodlands with shrubby understorey | +
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Eucalyptus low open woodlands with tussock grass OR Eucalyptus low -open woodlands with a shrubby understorey OR Eucalyptus low open -woodlands with a chenopod or samphire understorey | +
Plot type | ||
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Tropical Eucalypt Woodlands / Grasslands (MVG 12) | -Tropical Eucalyptus forests and woodlands with a tall annual grassy -understorey | +
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Acacia Open Woodlands (MVG 13) | -Mulga (Acacia aneura) open woodlands and sparse shrublands -+/- tussock grass OR Mulga (Acacia aneura) open woodlands and -sparse shrublands with hummock grass | +
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+
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Corner start point | +||
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Mallee Woodlands and Shrublands (MVG 14) | -Mallee with hummock grass OR Mallee with a tussock grass understorey -OR Mallee with a dense shrubby understorey OR Mallee with an open -shrubby understorey | +
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Low Closed Forest and Tall Closed Shrublands (MVG 15) | -Low closed forests or tall closed shrublands (including Acacia, -Melaleuca and Banksia) | +
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Acacia shrublands (MVG 16) | -Acacia (+/- low) open woodlands and sparse shrublands with a shrubby -understorey OR Acacia (+/- low) open woodlands and sparse shrublands -with hummock grass OR Acacia (+/- low) open woodlands and sparse -shrublands with tussock grass OR Acacia (+/- low) open woodlands and -sparse shrublands with chenopods. | +
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Other Acacia tall open shrublands and shrublands | +
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Sign type | +||
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Other Shrublands (MVG 17) | -Melaleuca shrublands and open shrublands OR Casuarina/Allocasuarina -shrublands (C. equisetifolia, A. littoralis, -A. verticillata) OR other shrublands | +
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Lignum shrublands and wetlands | +
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Heathlands (MVG 18) | -Heathlands | +
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Tussock Grasslands (MVG 19) | -Temperate tussock grassland | +
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Mitchell grass (Astrebla) tussock grasslands and Blue grass -(Dichanthium) and tall bunch grass (Chrysopogon) -tussock grasslands OR Other tussock grasslands | +
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Hummock Grasslands (MVG 20) | -Hummock grasslands | +
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Other Grasslands, Herblands, Sedgelands and Rushlands -(MVG 21) | -Sedgelands, rushes or reeds OR Wet tussock grasslands with herbs, -sedges or rushes, herblands or ferns OR Other grasslands | +
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Saline or brackish sedgelands or grasslands | +
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Chenopod Shrublands, Samphire Shrublands and Forblands -(MVG 22) | -Saltbush and/or Bluebush shrublands | +
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Mixed chenopod, samphire +/- forbs | +
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Mangroves (MVG 23) | -Mangroves (Northern) | +
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Mangroves (Southern) | +
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Other Open Woodlands (MVG 31) | -Callitris open woodlands OR Melaleuca open woodlands OR Other open -woodlands | +
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Sign age | +||
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Casuarina and Allocasuarina open woodlands with a shrubby -understorey OR Casuarina and Allocasuarina open woodlands with a -chenopod shrub understorey OR Casuarina and Allocasuarina open woodlands -with a tussock grass understorey OR Casuarina and Allocasuarina open -woodlands with a hummock grass understorey | +
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Mallee Open Woodlands and Sparse Mallee Shrublands (MVG 32) | -Open mallee woodlands and sparse mallee shrublands with a dense -shrubby understorey OR Open mallee woodlands and sparse mallee -shrublands with a sparse shrubby understorey OR Open mallee woodlands -and sparse mallee shrublands with a tussock grass understorey OR Open -mallee woodlands and sparse mallee shrublands with a hummock grass -understorey | +
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Age class | +
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Sign-based fauna surveys offer an indirect, non-invasive measure of + tern:purpose """
Sign-based fauna surveys offer an indirect, non-invasive measure of presence, abundance and impact, and are generally easy to undertake and require little specialised equipment or training. Sign-based measures -can be particularly useful for cryptic, nocturnal, elusive species or -species that occur in low abundance. In some instances, the signs left -by such species are more conspicuous than the animals themselves +can be particularly useful for cryptic, nocturnal and elusive species, +or species that occur in low abundance. In some instances, the signs +left by such species are more conspicuous than the animals themselves (Mitchell and Balogh 2007d, Claridge 2016, Indigo et al. 2021, Southwell et al. 2022). Sign-based surveys can be useful when direct observations -of fauna are not required or are difficult to obtain and to supplement +of fauna are not required or are difficult to obtain, and to supplement direct survey methods to get a more comprehensive understanding of distribution and abundance (Hone 1988, Mitchell and Balogh 2007d, Moriarty and Brown 2012, NPCA 2020).
-The Belt transect protocol is based on established methods and has -been adapted here to align with the 1 ha plot, to facilitate -comprehensive data analysis. A variation to the method is also available -and allows a more flexible approach over larger areas, where the user -specifies quadrat width, length, and number (minimum of 10 quadrats). -Longer transects are useful to understand broader scale trends across -the project area (based on the presence of signs) and undertake warren -and den counts.
-The 2 ha Arid Zone Monitoring (AZM) approach forms the basis of the -active plot search method, is well established and regularly used to -monitor the presence of arid zone fauna (Indigo et al. 2021). The data -are statistically robust and relatively inexpensive to measure but are -only applicable to monitoring the presence and distribution of fauna +
TheWithin-plot Belt Transect Protocol is based on established +methods and has been adapted here to align with the 1 ha Core Monitoring +Plot, to facilitate comprehensive data analysis. The Off-plot Belt Transect Protocol allows a more flexible approach over larger areas, +where the user specifies quadrat width, length, and number (minimum of +10 quadrats). Longer transects are useful to understand broader scale +trends across the project area (based on the presence of signs) and +undertake warren and den counts.
+The 2 ha Arid Zone Monitoring (AZM) approach, which forms the basis +of the Plot sign search protocol, is well established and regularly used +to monitor the presence of arid zone fauna (Indigo et al. 2021). The +data are statistically robust and relatively inexpensive to measure but +are only applicable to monitoring the presence and distribution of fauna rather than abundance (Southgate and Moseby 2008, Indigo et al. 2021). The tools and resources developed for the AZM, including a standard data collection template, workflow, and metadata have been integrated into -this module. The module offers a rapid approach (approximately -30 minutes per 2 ha area), suitable for use in the arid zone and can +the Plot Sign Search Protocol. AZM is a rapid approach (approximately 30 +minutes per 2 ha area) suitable for use in the arid zone and can document a range of fauna species. The method requires minimal training and no specialised equipment (Southgate and Moseby 2008, Indigo et al. -2021). A variation to this approach is also available for use in -non-arid systems. It aligns to the 1 ha fauna plot or the vegetation -plot, streamlining data collection where other modules are implemented -simultaneously.
-The Track count protocol offers a flexible, simple, cost-effective -(Fleming et al. 2014) and rapid approach (Edwards et al. 2000) for -population monitoring of species that have large home ranges (Wilson and -Delahay 2001). Track counts are effective for detecting cryptic and -elusive species because they do not require direct observation. They -capture the entire active period of a target species (e.g. capable of -detection over an entire 24-hour period) and can be conducted on vehicle -tracks, which can improve efficiency (Read and Eldridge 2010).
"""^^rdf:HTML ; - tern:scope """ -Prior to commencing any Sign-based Fauna Survey Module protocol, the +following should be completed:
+Familiarise yourself with the ecology of target fauna species and +the project area.
Assess the peak activity time of the target species to determine +the optimal survey period/s.
Determine habitat use preferences (e.g., dense vegetation, rugged +terrain) to aid with site selection.
Assess behaviour (e.g., elusive, utilises roads/tracks) to aid +with site selection.
Determine the access (e.g., vehicle tracks), terrain and +vegetation of the project area.
Determine the most appropriate survey design (i.e., within-plot +belt transects, off-plot belt transects, plot searches, vehicle tracks, +track stations, or a combination).
Identify potential survey sites using satellite imagery, spatial +datasets and on-ground knowledge of preferred habitat and signs of +target species, considering the location of any existing plots, +transects, vehicle tracks and track stations in the project +area.
Where transects will be used, identify potential start locations, +routes, and end locations. Ideally, transects should be a straight line +but may meander to adjust with landforms for ease of traversing +routes.
Where plot searches will be undertaken, identify potential plot +locations. Determine if a search area of 1 ha (Core Monitoring Plot or +Fauna Plot) or 2 ha (Biodiversity Plot) if appropriate.
Determine the survey frequency (i.e., monthly, bi-monthly, +quarterly, annually) and check that all survey areas will be accessible +for each survey period.
Ensure suitably experienced field staff are available for all +survey periods.
Ensure all necessary equipment is available and +operational.
Assess weather forecasts to ensure conditions are suitable. If +surveys are to be repeated over multiple days, ideally, the weather +should be similar for each survey.
Fauna can leave a range of signs in the landscape, and these signs can be used to detect their presence, quantify their relative abundance and assess impacts (Cowled and Lapidge 2004, Mitchell and Balogh 2007d, @@ -1363,35 +1363,219 @@ provides a standardised approach for surveying fauna signs. The module is best suited for rabbits, wild dogs, foxes, feral pigs, cats, deer, and goats, but it can be used for other species of interest, including camel, horses and non-pest fauna species.
-The key attributes recorded during the completion of this module -include:
+The key attributes recorded by this module include:
Presence/absence of each sign type, and attributable species, for -each quadrat.
Count of each sign, and attributable species, for each quadrat -(optional).
Removal of scats once counted in each quadrat, allowing for an -accumulated rate to be surveyed on subsequent revisits -(optional).
Presence of each sign type and attributable species.
Absence of signs from quadrats in the belt transect +protocols.
Count of each sign (optional).
Accumulation rate of scats by removing counted scats from +quadrats in the belt transects protocol and conducting subsequent +revisits (optional).
Age of the signs (optional).
Types of fauna signs that should be recorded include:
+Types of fauna signs that can be recorded include, but are not +limited to:
Track
Scat and dung
Dung heap
Nest
Rub on fence posts
Tracks
Scats and dungs
Dung heaps
Nests
Rubs on fence posts
Shed antlers
Prey item discards (including partly consumed animals or removed body parts)
Deceased individuals.
If the project is primarily concerned with the extent of herbivory -and physical damage, (digging, wallowing, browse rubbing, etc.), -complete the Herbivory and Physical Damage Module.
"""^^rdf:HTML ; +and physical damage (digging, wallowing, browse rubbing, etc.), complete +the Herbivory and Physical Damage Module. +Pest fauna | +Recommended approach | +Transect length and width | +Active period | +Other comments / considerations | +Key resources | +
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Feral cat | +Continuous transect/track plots along a transect. | ++ |
++ |
++ |
++ |
+
Fox | +Continuous transect/track plots along a transect. | ++ |
++ |
++ |
++ |
+
Wild dog | +Continuous transect/track plots along a transect. | ++ |
++ |
++ |
++ |
+
Rabbit | +Belt transect/continuous transect. | ++ |
++ |
++ |
++ |
+
Feral deer | +Circular plots along a transect/belt transect. | ++ |
++ |
++ |
++ |
+
Feral goat | +2 ha active search/belt transect. | ++ |
++ |
++ |
++ |
+
Feral pig | +Track plots along a transect. | ++ |
++ |
++ |
++ |
+
Pre-requisites for completing this protocol:
+None.
Survey activity time estimates will vary depending on the number and -variety of signs encountered, the number of measures recorded, and if -scats are being collected and removed or merely recorded. As a general -guide:
+Survey activity time estimates will vary depending on the length of +the transect, the number and variety of signs encountered, the number of +measures recorded, and if scats are being collected and removed or +merely recorded. As a general guide:
Allow 1–2 hours hour for survey planning.
Allow 20–60 minutes to complete the reconnaissance visit and @@ -49,9 +51,9 @@ species. If surveyors are not confident, time should be dedicated to practising, using field reference guides, and seeking advice before conducting this protocol.
Within-plot belt transects do not involve interference with -wildlife. Therefore scientific permits and wildlife ethics approvals are -unlikely to be required, but remember to always check with your local -authority. Access permissions are required.
ACT Government. 2015. Best Practice Management Guide for Rabbits in @@ -87,7 +89,7 @@ spatial patterns of defecation in wild boar. Wildlife Society Bulletin M. N. Gentle, L. J. McLeod, P. D. Meek, and G. R. Saunders. 2014. Management of wild canids in Australia: free-ranging dogs and red foxes. Pages 105–149 in A. Glen and C. Dickman, editors. Carnivores of -Australia: Past, Present and Future. CSIRO Publishing, Collingwood, +Australia: past, present and future. CSIRO Publishing, Collingwood, Victoria.
Higashide, D., T. Kuriyama, S. Takagi, Y. Nakashima, K. Fukasawa, G. Yajima, M. Kasada, and M. Yokoyama. 2021. Effectiveness of signs of @@ -111,9 +113,6 @@ Energy. Department of the Environment and Energy, Canberra.
Kennedy, M., B. L. Phillips, S. Legge, S. A. Murphy, and R. A. Faulkner. 2012. Do dingoes suppress the activity of feral cats in northern Australia? Austral Ecology 37:134-139.
-Koichi, K., D. Holliday, and C. e. Harris. 2020. Glovebox Guide for -Managing Feral Pigs v2.0. PestSmart Toolkit publication., The Centre for -Invasive Species Solutions, Canberra ACT.
Masters, P., N. Markopoulos, B. Florance, and R. Southgate. 2018. The eradication of fallow deer (Dama dama) and feral goats (Capra hircus) from Kangaroo Island, South Australia. @@ -162,7 +161,7 @@ Network at WWF Australia, Sydney.
Backhouse, K. Bellchambers, R. Brandle, P. Brenton, and P. Copley. 2022. Designing a large‐scale track‐based monitoring program to detect changes in species distributions in arid Australia. Ecological -Applications:e2762. +applications:e2762.Threatened Species Recovery Hub. undated. Data collection in track-based surveys.
Triggs, B. 1996. Tracks, scats and other traces. A field guide to @@ -178,9 +177,11 @@ planning
There is no limitation to the length of transects. However, transect lengths are typically restricted to personnel resources, -logistics of completing the surveys, and the window of opportunity to -survey under the same weather conditions. As a guide, transects should -be a minimum of 1 km in length.
Surveys should only be conducted in good weather conditions, when temperature, wind and rainfall are typical for the season. Poor weather @@ -213,10 +214,10 @@ sway) the morning of the survey, consider rescheduling.
There is no rule for when to repeat surveys. Surveys should be -conducted as often as the project requires, i.e. weekly, monthly, +conducted as often as the project requires, i.e., weekly, monthly, bi-monthly, quarterly. For consistency, aim to replicate the conditions, -i.e. similar weather, similar time, moon phase, observers, and reference -materials.
Weather conditions should be recorded at least once per day, but can be recorded multiple times, if weather conditions change.
Scats can be left in situ or removed during the survey to allow for a faecal accumulation rate to be calculated on future surveys -(optional) (Engeman et al. 2013) (Engeman et al. 2013, Ferretti et al. -2015).
If scats are removed they should be picked up by hand (gloves are -recommended), bagged and moved away from the transect line or any other -transect lines that are being surveyed or may be surveyed in the future. -Scats can be moved to the outer edge of the plot away from other +(optional) (Engeman et al. 2013, Ferretti et al. 2015).
If scats are removed, they should be picked up by hand (gloves +are recommended), bagged and moved away from the transect line or any +other transect lines that are being surveyed or may be surveyed in the +future. Scats can be moved to the outer edge of the plot away from other transect lines. Do not create excessive disturbance by raking or sweeping the scats.
Warrens and dens are recorded as being present, and active or in-active entrances within each quadrat are recorded (optional). There -is no need to count the number of entrances in each quadrat, or note -each entrance's active or in-active status.
Active burrows have an entrance that is not blocked by spiderwebs or vegetation, usually with tracks, scrapings and/or scats at the entrance. Some animals have burrow systems with multiple entrances, some @@ -300,121 +300,1087 @@ fine features of tracks disappear, and only the general gait is visible.
As scats age, they become drier, lighter in colour, and get harder and less smelly. Very old scats are crumbly and do not -smell.
Complete lists are provided in the Monitor app, as well as the TERN +website.
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General:
Mobile device with the Monitor app installed
GNSS, such as a Trimble R1 or DA2 receiver, a hand-held GPS or -device built-in GPS (least preferred), capable of achieving <30 cm -accuracy
Mobile device (tablet/phone) with the Monitor app +installed
GNSS receiver capable of achieving <30 cm accuracy (e.g., +Trimble R1 or DA2), hand-held GPS, or device built-in GPS (least +preferred)
Field guides for identifying signs to species level
Scale card
100 m tape measure
1 m pole or retractable 5–10 m tape measure.
Survey pole or pocket tape measure.
For removal of scats for faecal accumulation rates:
Gloves
Bags for temporarily holding scats for removal.
Arrive at the pre-identified survey location and ensure habitats -represent the project area.
Check the transect route and ensure the length is traversable in -all weather conditions. Identify any safety hazards. If necessary, amend -the transect start location, route and end location that was -pre-determined.
Complete the Vegetation Mapping Module along or near the transect -to record relevant habitat information.
Open the Monitor app and select Sign-based Fauna Survey -Module > Off-plot belt transects protocol.
Select either an existing transect and choose the -applicable transect ID code from the drop-down list or select create -new transect.
Select survey intent using the drop-down (once-off + tern:instructions """
Conduct a reconnaissance field survey to identify which potential +survey sites (and any others sites not identified during pre-survey +planning) are suitable transect locations. Ensure habitats are +representative of the project area.
For each proposed transect, check the route and ensure the entire +length is traversable in all weather conditions. Ideally, transects +should be a straight line but may meander to adjust with landforms for +ease of walking routes. Identify the best direction of travel and any +safety hazards.
Determine the transect start locations, routes and end +locations.
Travel to a transect start location to a begin a transect and +survey set-up.
If using an external GNSS/GPS, ensure it is turned on and +connected to the mobile/tablet.
Open the Monitor app and select the Sign-based Fauna Survey +Module and then the Off-plot belt transects protocol.
Select create new transect to assign a new transect +ID. If conducting a repeated measure of an established transect, +select existing transect and select the relevant transect +ID from the dropdown, then skip to step 7.
Record the transect information, including:
Transect start location – recorded automatically. Update +if required.
Date – the date and time that the +transect is established is automatically recorded. Update if +required.
Route type – select a value that best represents the +transect from the dropdown (vehicle road, vehicle dirt track, walking +track, off-track no defined path) or input a custom value.
Transect alignment (°) – based on the direction of +travel.
Quadrat width – between 1–4 m (see guidelines for +recommended quadrat dimensions).
Quadrat length – along the tape, between 1–20 m (see +guidelines for recommended quadrat dimensions).
Transect length (m) –only numbers divisible by the +quadrat length will be accepted.
Transect spacing (m) – distance between transects +(optional, can be updated using spatial data if required).
Habitat (Major Vegetation Group) – select the Major +Vegetation Group that best represents the transect. This is an optional +field and should be completed if no monitoring plots or mapped locations +using the Vegetation Mapping Module have been completed along or in the +vicinity of the transect.
Save the transect. Additional transects can be added by selecting +the add button (if the workflow involves setting up all transects prior +to conducting surveys.
Record the survey information:
Survey set-up ID – select the relevant transect +ID to assign a new survey set-up ID (transect +ID-date).
Survey intent – indicate if survey intent is once-off measure, repeated measure, linked to a pre-control activity or -post-control activity, other). If other is selected, record the intent -using the text box.
Select the data types that will be recorded for each -quadrat (sign presence only, sign presence by attributable species, -count of each sign, count of each sign by attributable species, age of -sign).
Indicate if scats will be counted and left in situ or -if scats will be removed using the check-box.
Enter the number of observers participating in the -survey, and for each observer, enter the observer name and -observer role (spotter, data entry, data entry only).
Enter the weather conditions, including temperature, -rainfall, rainfall duration, cloud cover, wind speed, and moon -phase of the previous night. The weather conditions can be adjusted -after the survey.
Enter the transect route type that best represents the -transect (vehicle road, vehicle dirt track, walking track, off-track no -defined path, or other). If other is selected, record the applicable -route type in the text box.
Enter the transect direction compass bearing.
Enter the quadrat width (between 1 and 4 m), and the -quadrat length (along the tape) between 1 and 20 m.
Target species – select the target species (e.g., Cat, +Fox, Wild dog, Rabbit, Deer species, Goat, Pig, Horse, Camel). Select +‘Other’ to specify a species not in the dropdown. Multiple species can +be selected/specified.
Scat removal – indicate if scats will be counted and +left in situ or if scats will be removed using the +check-box.
Tracking substrate – select from the drop-down (sand, +gravel, mud) or input a custom value.
Observer details – enter details for each observer, +including the observer name and observer role +(spotter, data entry). Multiple roles can be selected for each +observer.
Weather conditions – including temperature, +rainfall, rainfall duration, cloud cover, +wind description, and moon phase. Note the weather +conditions can be adjusted at the completion of the survey.
Save the survey information. Survey information for additional +transects can be added by selecting the add button (if the workflow +involves setting up all surveys prior to conducting surveys.
Install a peg into the end of a tape measure and run out the 100 m tape measure in a straight line following the compass bearing towards the intended endpoint.
Once all observers are ready and tape measure is in place, return +to the start position and complete the survey set-up component and +follow the conduct the survey steps below.
Once all observers are ready and the tape measure is in place, -return to the transect start position and select commence -survey.
Select take transect 1 start photo. Next, hold the -device in front of you and take a landscape-orientated photo looking -along the transect.
Select start transect 1. The time and date will -automatically be recorded.
Stand on the left side of the tape, at 0 m, hold the 5-10 m -retractable tape or measuring pole horizontally and at right angles to -the tape. Begin to walk parallel to the tape line so one end of the pole -roughly follows the tape, and the other end aids as a visual clue to -identify the area of the quadrat (Figure 1).
Figure 1. Plot layouts for the 100 x 100 m core plot 40 x 40 m sub-plot showing -available transects.
--
The starting point along the transect will depend on the quadrat -dimensions pre-selected. For the preceding quadrat area select If signs -were present or absent using the check-box.
Where signs are present, for each sign observed, select add -sign and record:
Select the survey set-up ID based on the relevant +transect ID and associated survey set-up.
Take a transect photo. Hold the device in front of you +and take a landscape-orientated photo looking along the +transect.
Select start transect. The transect start +location and survey start time will be automatically +recorded.
Stand on the left side of the transect at 0 m. Hold the pocket +tape measure (locked at the width of the quadrat) or measuring pole +horizontally and at a right angle to the transect. Begin to walk +parallel to the transect so one end of the pocket tape/pole follows the +100 m tape, and the other end provides a visual aid to identify the area +of quadrat (Figure 2).
At each quadrat interval along the transect, starting at the +distance pre-selected as for quadrat length, enter the +quadrat number and record for the preceding quadrat if signs +are present or absent using the check-box.
Figure 2. Surveyor holding a tape measure at 1 m to indicate the edge of the quadrat being assessed for signs of fauna.
+Where signs are present, record:
the sign type (scat, track, dig, burrow, warren, -other).
the attributable fauna species (cat, fox, wild dog, -rabbit, deer species, goat, pig, horse, camel, other, unknown).
the sign age (fresh 1-2 days, old 3-7 days, very old 7+ -days). (optional field)
the age class of the attributable species (juvenile or -adult). (optional field)
the count (number of the type of sign) within the -quadrat. If the count for rabbit pellets observed exceeds 40, it should -instead be recorded as a buck-heap using the check-box. If -warren is the type of sign observed record if it is active or -not active using the check-box.
add a representative photo of the sign. Not all signs +
Location – recorded automatically. Update if +required.
Sign type – select from the drop-down (tracks, scats, +dens, buck heaps, warrens, burrows, diggings, wallows, ground rooting, +rubs roll pits, pugging) or input a custom value. If the sign type is +den, warren or burrow, record if it is +active or not active using the check-box.
Number of entrances – if the sign type is den, +warren or burrow, record the number of +entrances.
Attributable fauna species – select from the drop-down +(cat, fox, wild dog, rabbit, deer species, goat, pig, horse, camel, +unknown) or input a custom value.
Sign age – record is the sign is fresh 1–2 days, old 3–7 +days or very old 7+ days (optional field).
Age class – record if the attributable species is a +juvenile or adult (optional field).
Count – record the number of the type of sign within the +quadrat. If the count for rabbit pellets observed exceeds 40, record the +sign type as buck-heap and count as 1.
Add a representative photo of the sign. Not all signs observed need to be photographed provided there is one photograph of each sign type. A scale card should be used in all photos. (optional -field)
add any additional comments in the text box.
Add any comments.
Repeat steps 19-20 at each quadrat along the transect. When you -reach the end of the tape measure, select end -transect.
To add additional belt transects select add transect. -You will be prompted to create and set-up a new transect.
Once the desired number of transects are complete, select -complete belt transect survey.
Save the observation. If another observation for the same quadrat +is to be recorded select the add button. When observations for a quadrat +are complete, select save and next quadrat.
Repeat steps 5–7 at each quadrat along the transect.
If you reach the end of the tape measure before the end of the +transect, add another tape by inserting a peg into the end of the tape +measure, and following the compass baring run out the tape measure +before returning to the start of that tape to recommence the +transect.
Once you reach the end of the belt transect, select end +transect. The transect end location and survey end +time will be automatically recorded.
For each additional transect, repeat the transect and survey +set-up and conduct the survey steps.
Once all transects have been completed, complete the transect +survey component.
Queue the collection for submission.
If conducting repeated measures within the current visit, repeat +the entire process and create a new collection, selecting from existing +transects in the transect and survey set-up step.
Pre-requisites for completing this protocol:
The plot must be established using the Plot Selection and Layout -Module prior to, or during the reconnaissance survey of the Active plot +
The plot must be established using the Plot Selection and Layout Module prior to, or during the reconnaissance survey of the Active plot search protocol.
The Plot Description Module must be completed prior to, or during the reconnaissance survey the Active search protocol.
Personnel number and skills:
+Within-plot belt transects are best conducted with two personnel, one +making the observations and one recording the data directly into the +app.
Within-plot belt transects are best conducted with two personnel, -one making the observations and one recording the data directly into the -app.
The surveyor making the observations should be familiar with and experienced in identifying the characteristic identifiable features of the target species signs and how to distinguish these signs from other @@ -57,9 +54,9 @@ species. If surveyors are not confident, time should be dedicated to practising, using field reference guides, and seeking advice before conducting this protocol.
Within-plot belt transects do not involve interference with -wildlife. Therefore scientific permits and wildlife ethics approvals are -unlikely to be required, but remember to always check with your local -authority. Access permissions are required.
ACT Government. 2015. Best Practice Management Guide for Rabbits in @@ -95,7 +92,7 @@ spatial patterns of defecation in wild boar. Wildlife Society Bulletin M. N. Gentle, L. J. McLeod, P. D. Meek, and G. R. Saunders. 2014. Management of wild canids in Australia: free-ranging dogs and red foxes. Pages 105–149 in A. Glen and C. Dickman, editors. Carnivores of -Australia: Past, Present and Future. CSIRO Publishing, Collingwood, +Australia: past, present and future. CSIRO Publishing, Collingwood, Victoria.
Higashide, D., T. Kuriyama, S. Takagi, Y. Nakashima, K. Fukasawa, G. Yajima, M. Kasada, and M. Yokoyama. 2021. Effectiveness of signs of @@ -119,9 +116,6 @@ Energy. Department of the Environment and Energy, Canberra.
Kennedy, M., B. L. Phillips, S. Legge, S. A. Murphy, and R. A. Faulkner. 2012. Do dingoes suppress the activity of feral cats in northern Australia? Austral Ecology 37:134-139.
-Koichi, K., D. Holliday, and C. e. Harris. 2020. Glovebox Guide for -Managing Feral Pigs v2.0. PestSmart Toolkit publication., The Centre for -Invasive Species Solutions, Canberra ACT.
Masters, P., N. Markopoulos, B. Florance, and R. Southgate. 2018. The eradication of fallow deer (Dama dama) and feral goats (Capra hircus) from Kangaroo Island, South Australia. @@ -170,7 +164,7 @@ Network at WWF Australia, Sydney.
Backhouse, K. Bellchambers, R. Brandle, P. Brenton, and P. Copley. 2022. Designing a large‐scale track‐based monitoring program to detect changes in species distributions in arid Australia. Ecological -Applications:e2762. +applications:e2762.Threatened Species Recovery Hub. undated. Data collection in track-based surveys.
Triggs, B. 1996. Tracks, scats and other traces. A field guide to @@ -183,13 +177,13 @@ observation. Wildlife Research 28:151-164.
"""^^rdf:HTML ;Plot sign searches can be conducted at core 1 ha plots (where -other modules have been completed), at fauna plots (where other fauna -based modules have been completed), or at 2 ha biodiversity plots -(combining both core and fauna plots for a total of 2 ha), however -consideration needs to be given to the timing of the surveys. Activity -should be minimised immediately prior and during a trapping survey to -reduce disturbance.
Plot sign searches can be conducted at 1 ha Core Monitoring Plots +(where other modules have been completed), at 1 ha Fauna Plots (where +other fauna-based modules have been completed), or at 2 ha Biodiversity +Plots (combining both Core Monitoring and Fauna Plots for a total of 2 +ha), however consideration needs to be given to the timing of the +surveys. Activity should be minimised immediately prior and during a +trapping survey to reduce disturbance.
Assess the overall survey location to ensure that the substrate offers a suitable tracking surface across a broad area for detecting tracks and other signs (soft sand, not too much vegetation, soil crust @@ -198,10 +192,9 @@ using the Plot sign search protocol, and the signs Within-plot belt transect protocol is more appropriate.
Plots where sign searches are conducted should be a minimum of 4 km apart.
If an associated road transect is also surveyed, it should be -100 m in length. A 100 m measuring tape can be used or it can be defined -using the app. A 100 m transect is used, irrespective of plot size (i.e. -same for 2 ha and 1 ha plots).
If an associated road transect is also surveyed, it should be 100 +m in length. A 100 m transect is used, irrespective of plot size (i.e., +same for 2 ha and 1 ha plots).
Surveys should only be conducted in good weather conditions, when temperature, wind and rainfall are typical for the season. Poor weather @@ -232,10 +225,10 @@ sway) the morning of the survey, consider rescheduling.
There is no rule for when to repeat surveys. Surveys should be -conducted as often as the project requires, i.e. weekly, monthly, +conducted as often as the project requires, i.e., weekly, monthly, bi-monthly, quarterly. For consistency, aim to replicate the conditions, -i.e. similar weather, similar time, moon phase, observers, and reference -materials.
Weather conditions should be recorded at least once per day, but can be recorded multiple times, if weather conditions change.
The best tracks are found early in the morning and are easiest to observe with the shadow behind the observer (Triggs 1996, Moseby et al. -2009).
Walk into the sun when recording tracks to optimise shadows (Arid Zone Monitoring 2021).
Don’t depend on a single print for identification of a species, @@ -284,12 +277,11 @@ collection each quadrat (optional).
Scats can be left in situ or removed during the survey to allow for a faecal accumulation rate to be calculated on future surveys -(optional) (Engeman et al. 2013) (Engeman et al. 2013, Ferretti et al. -2015).
If scats are removed they should be picked up by hand (gloves are -recommended), bagged and moved away from the transect line or any other -transect lines that are being surveyed or may be surveyed in the future. -Scats can be moved to the outer edge of the plot away from other +(optional) (Engeman et al. 2013, Ferretti et al. 2015).
If scats are removed, they should be picked up by hand (gloves +are recommended), bagged and moved away from the transect line or any +other transect lines that are being surveyed or may be surveyed in the +future. Scats can be moved to the outer edge of the plot away from other transect lines. Do not create excessive disturbance by raking or sweeping the scats.
Warrens and dens are recorded as being present, and active or in-active entrances within each quadrat are recorded (optional). There -is no need to count the number of entrances in each quadrat, or note -each entrance's active or in-active status.
Active burrows have an entrance that is not blocked by spiderwebs or vegetation, usually with tracks, scrapings and/or scats at the entrance. Some animals have burrow systems with multiple entrances, some @@ -324,17 +316,18 @@ smell.
Appendix 1. Data -collection fields from the Signs-based Fauna Survey Module
Complete lists are provided in the Monitor app, as well as the TERN -website
+website.Transect route type | +Route type |
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Survey intent | +Survey intent |
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Target species | +Target species |
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Survey type | +Tracking substrate |
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Observer role | +Track station substrate |
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Micro-habitat | +|
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Weather conditions | +Habitat (Major Vegetation Group) |
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Sign type* (not a complete list) | +Weather conditions |
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NVIS Major Vegetation Group | -NVIS Major Vegetation Sub-group | -|
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Rainforest and Vine Thickets (MVG 1) | -Cool temperate rainforest | +
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Tropical or sub-tropical rainforests | +
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Dry rainforest | +
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Vine thickets | +
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Eucalypt Tall Open Forests (MVG 2) | -Eucalyptus tall open forests with a dense broad-leaved and/or -tree-fern understorey (wet-sclerophyll) | +
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Eucalyptus tall open forests with a fine-leaved shrubby understorey -OR Eucalyptus tall open forests and open forests with ferns, herbs, -sedges, rushes or wet tussock grasses | +
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Eucalypt Open Forests (MVG 3) | -Eucalyptus open forests with a shrubby understorey | +
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Eucalyptus open forests with a grassy understorey | +
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Eucalypt Low Open Forests (MVG 4) | -- | +
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Eucalypt Woodlands (MVG 5) | -Eucalyptus woodlands with a shrubby understorey OR Eucalyptus -woodlands with a chenopod or samphire understorey | +
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Eucalyptus woodlands with a grassy understorey OR Eucalyptus -woodlands with ferns, herbs, sedges, rushes or wet tussock grassland OR -Eucalyptus woodlands with a hummock grass understorey | +
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Acacia Forests and Woodlands (MVG 6) | -Brigalow (Acacia harpophylla) forests and woodlands | +
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Other Acacia forests and woodlands | +
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Mulga (Acacia aneura) woodlands and shrublands +/- tussock -grass +/- forbs OR Mulga (Acacia aneura) woodlands and -shrublands with hummock grass | +
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Callitris Forests and Woodlands (MVG 7) | -Callitris forests and woodlands (Eastern occurrence) | +
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Callitris forests and woodlands (mallee, arid and semi-arid -occurrence) | +
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Casuarina Forests and Woodlands (MVG 8) | -Casuarina and Allocasuarina forests and woodlands | +
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River Oak forests and woodlands | +
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Melaleuca Forests and Woodlands (MVG 9) | -Melaleuca open forests and woodlands | +
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Other Forests and Woodlands (MVG 10) | -Other forests and woodlands OR Banksia woodlands OR Leptospermum -forests and woodlands OR Tropical mixed species forests and -woodlands | +
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Eucalypt Open Woodlands (MVG 11) | -Eucalyptus open woodlands with a grassy understorey OR Eucalyptus -open woodlands with shrubby understorey | +
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Eucalyptus low open woodlands with tussock grass OR Eucalyptus low -open woodlands with a shrubby understorey OR Eucalyptus low open -woodlands with a chenopod or samphire understorey | +
Plot type | ||
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Tropical Eucalypt Woodlands / Grasslands (MVG 12) | -Tropical Eucalyptus forests and woodlands with a tall annual grassy -understorey | +
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Acacia Open Woodlands (MVG 13) | -Mulga (Acacia aneura) open woodlands and sparse shrublands -+/- tussock grass OR Mulga (Acacia aneura) open woodlands and -sparse shrublands with hummock grass | +
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Mallee Woodlands and Shrublands (MVG 14) | -Mallee with hummock grass OR Mallee with a tussock grass understorey -OR Mallee with a dense shrubby understorey OR Mallee with an open -shrubby understorey | +
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Corner start point | +||
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Low Closed Forest and Tall Closed Shrublands (MVG 15) | -Low closed forests or tall closed shrublands (including Acacia, -Melaleuca and Banksia) | +
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Acacia shrublands (MVG 16) | -Acacia (+/- low) open woodlands and sparse shrublands with a shrubby -understorey OR Acacia (+/- low) open woodlands and sparse shrublands -with hummock grass OR Acacia (+/- low) open woodlands and sparse -shrublands with tussock grass OR Acacia (+/- low) open woodlands and -sparse shrublands with chenopods. | +
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Other Acacia tall open shrublands and shrublands | +
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Sign type | +||
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Other Shrublands (MVG 17) | -Melaleuca shrublands and open shrublands OR Casuarina/Allocasuarina -shrublands (C. equisetifolia, A. littoralis, -A. verticillata) OR other shrublands | +
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Lignum shrublands and wetlands | +
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Heathlands (MVG 18) | -Heathlands | +
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Tussock Grasslands (MVG 19) | -Temperate tussock grassland | +
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Mitchell grass (Astrebla) tussock grasslands and Blue grass -(Dichanthium) and tall bunch grass (Chrysopogon) -tussock grasslands OR Other tussock grasslands | +
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Hummock Grasslands (MVG 20) | -Hummock grasslands | +
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Other Grasslands, Herblands, Sedgelands and Rushlands -(MVG 21) | -Sedgelands, rushes or reeds OR Wet tussock grasslands with herbs, -sedges or rushes, herblands or ferns OR Other grasslands | +
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Saline or brackish sedgelands or grasslands | +
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Chenopod Shrublands, Samphire Shrublands and Forblands -(MVG 22) | -Saltbush and/or Bluebush shrublands | +
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Mixed chenopod, samphire +/- forbs | +
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Mangroves (MVG 23) | -Mangroves (Northern) | +
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Mangroves (Southern) | +
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Other Open Woodlands (MVG 31) | -Callitris open woodlands OR Melaleuca open woodlands OR Other open -woodlands | +
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Sign age | +||
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Casuarina and Allocasuarina open woodlands with a shrubby -understorey OR Casuarina and Allocasuarina open woodlands with a -chenopod shrub understorey OR Casuarina and Allocasuarina open woodlands -with a tussock grass understorey OR Casuarina and Allocasuarina open -woodlands with a hummock grass understorey | +
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Mallee Open Woodlands and Sparse Mallee Shrublands (MVG 32) | -Open mallee woodlands and sparse mallee shrublands with a dense -shrubby understorey OR Open mallee woodlands and sparse mallee -shrublands with a sparse shrubby understorey OR Open mallee woodlands -and sparse mallee shrublands with a tussock grass understorey OR Open -mallee woodlands and sparse mallee shrublands with a hummock grass -understorey | +
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Age class | +
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General:
Mobile device with the Monitor app installed
GNSS, such as a Trimble R1 or DA2 receiver, a hand-held GPS or -device built-in GPS (least preferred), capable of achieving <30 cm -accuracy
Mobile device (tablet/phone) with the Monitor app +installed
GNSS receiver capable of achieving <30 cm accuracy (e.g., +Trimble R1 or DA2), hand-held GPS, or device built-in GPS (least +preferred)
Field guides for identifying signs to species level
Scale card
100 m tape measure
1 m pole or builders tape measure set to 1 m (See Appendix -1)
For removal of scats for faecal accumulation rates:
-Survey pole or pocket tape measure.
+For removal of scats for faecal accumulation rates:
Gloves
Bags for temporarily holding scats for removal.
Arrive at the plot prior to the intended survey date. Traverse -the plot to assess vegetation cover, density, and substrate. Assess the -surface condition to ensure areas of bare sand are present and the plot -is not covered in vegetation cover or leaf litter. If the plot does not -have areas suitable for tracking, do not proceed and instead consider -using the Within-plot belt transect protocol.
If suitable, arrive at the plot on the day of the survey, ideally -early morning or late afternoon.
Traverse the plot to assess vegetation cover, density, and +substrate. Assess the surface condition to ensure areas of bare ground +are present and the plot is not covered in vegetation or leaf litter. If +the plot does not have areas suitable for tracking, do not proceed and +instead consider using the Within-plot belt transect protocol.
If using an external GNSS/GPS, ensure it is turned on and +connected to the mobile/tablet.
Ensure the Plot Selection and Layout Module has been completed to -mark out the plot boundary and define the current visit in the Monitor -app.
Ensure the Standard protocol within the Plot Description Module -has been completed.
Open the Monitor app and select Sign-based Fauna Survey -Module > Active plot sign search protocol.
Open the Monitor app and select the Sign-based Fauna Survey +Module and then the Active plot sign search protocol.
Indicate if survey intent is a once-off measure, -repeated measure, repeated measure with previous scat removal, or linked -to a pre-control activity or post-control activity (optional).
Indicate if a nearby track transect survey will be -conducted after the plot has been completed.
Indicate the target species for the survey (cat, fox, -wild dog, rabbit, deer species, goat, pig, horse, camel, other). -Multiple species can be selected. If other is selected, enter the pest -species name.
Enter the number of observers, observer name -and observer role (spotter, data entry, data entry only) for -each observer.
Enter the weather conditions, including -temperature, rainfall, rainfall duration, cloud -cover, wind speed, and moon phase of the previous -night. Note the weather conditions can be adjusted after the -survey.
Enter the tracking surface information including -detectability of the tracking surface type.
Identify if site information will be completed after the -survey has been conducted or if other modules are being conducted in -unison, whereby site information such as floristics and habitat -condition will be collected elsewhere (refer to guidelines for further -information).
Indicate if a nearby transect track survey will be +conducted after the plot has been completed.
Indicate the target species (Cat, Fox, Wild dog, Rabbit, +Deer species, Goat, Pig, Horse, Camel). Select ‘Other’ to specify a +species not in the dropdown. Multiple species can be selected/specified. +If there are no target species for this project, select +N/A.
Record the tracking substrate (sand, gravel, mud) or +input a custom value.
Indicate if scats will be counted and left in situ or if +scats will be removed using the check-box.
For each observer, enter the observer name and +observer role (spotter, data entry).
Enter the weather conditions, including temperature, +rainfall, rainfall duration, cloud cover, wind descripition, and moon +phase. Note the weather conditions can be adjusted at the +completion of the survey. Complete the survey set-up component.
Arrive at the plot and identify the position of the sun. Next, -determine which direction to commence traversing the plot, ideally -walking into the sun to use shadows cast by tracks, and identify which -corner of the plot to start the survey at (either of the 4 -corners).
Select record start location and select the corner you -are standing at to commence the survey. The app will record the -location, start date and time automatically. For subsequent re-surveys, +
Record the plot type (Core Monitoring Plot (1 ha), Fauna +Plot (1 ha), Biodiversity Plot (2 ha)).
Determine which direction to commence traversing the plot, +ideally walking into the sun to use shadows cast by tracks, and identify +which corner of the plot to start the survey at (NE, NW, SE, +SW).
Select record start location and select the corner +start point you are standing at to commence the survey. The app +will record the location, start date and time +and commence the survey timer automatically. For subsequent re-surveys, make sure the survey starts at the same corner so that start location photos are the same.
Select start location photo and face towards the centre of the plot to take a representative photo.
Select start active sign search to commence the timer, -then begin surveying by zig-zagging across the plot looking for signs. -Your position within the plot will be shown, and the app will record a -location every minute until the survey is completed, creating a trail -across the plot. Ensure the entire plot is covered by checking the map -intermittently, even when no signs are observed.
For each sign observed, select add sign record:
Select start plot sign search to commence the timer, +then begin surveying in a zig-zag fashion across the plot looking for +signs. Your position within the plot will be shown, and the app will +record a location every minute until the survey is completed, creating a +trail across the plot. Ensure the entire plot is covered by checking the +map intermittently using the track log button even when no +signs are observed.
For each sign observed, select add sign and +record:
Location –the location of the observation is +automatically recorded when add sign is selected. Update if +required.
Date – the date and time of the +observation is automatically recorded when add sign is +selected. Update if required.
Sign type – select from the drop-down (tracks, scats, +dens, buck heaps, warrens, burrows, diggings, wallows, ground rooting, +rubs roll pits, pugging) or input a custom value. If the sign type is +den, warren or burrow, record if it is +active or not active using the check-box.
Number of entrances – if the sign type is den, +warren or burrow, record the number of +entrances.
select the sign type (scat, track, dig, burrow, warren, etc, see -Appendix 1)
select the attributable fauna species (select unknown if not -certain)
indicate the sign age (fresh 1-2 days, old 3-7 days, very old 7+ -days) (optional field)
indicate the age class of the individual responsible for the sign -(optional field applicable to scats and tracks only based on -size)
add photo (representative photos should be taken for each -species/sign type for the plot – i.e. not all signs observed need to be -photographed, ideally a scale card should be used in all photos -(optional, up to 3 photos per sign record)
if warrens, burrows or dens are observed, count and record the -number of entrances and record if any are considered active or not -active (optional)
add any additional comments in the observation comments field. -Recording the gait length and width may be of interest, particularly of -feral cats and foxes to assist distinguishing individuals.
Attributable fauna species – select from the drop-down +(cat, fox, wild dog, rabbit, deer species, goat, pig, horse, camel, +unknown) or input a custom value.
Sign age – record is the sign is fresh 1–2 days, old 3–7 +days or very old 7+ days (optional field).
Age class – record if the attributable species is a +juvenile or adult (optional field).
+Count – record the number of the type of sign within the +quadrat. If the count for rabbit pellets observed exceeds 40, record the +sign type as buck-heap and count as 1.
Add a representative photo of the sign. Not all signs +observed need to be photographed provided there is one photograph of +each sign type. A scale card should be used in all photos. (optional +field).
Add any comments. Recording the gait length and width +may be of interest, particularly of feral cats and foxes to assist +distinguishing individuals.
Traverse the entire plot area recording all signs observed.
The active search is complete when the surveyors are confident the entire plot has been searched, and there has been a minimum of 60 minutes survey effort. Remember to check the app screen to identify any areas missed. There is no time limit (see below for recommendations).
Once the active search is complete, select end active -search. Edit any key information (i.e. adjust the weather +search. The survey end time will be recorded +automatically. Edit any key information (e.g., adjust the weather conditions, particularly if wind or light conditions changed during the survey).
The optional nearby track plot option will only be displayed in the -app if add nearby track transect was selected during the survey -set-up stage (see above). This optional survey component should only be -completed if a suitable section of the nearby vehicle track occurs -within 200 m of the plot just surveyed, and if it safe to survey (i.e. -no expected vehicles).
-Arrive at the intended section of a nearby track.
Select set-up nearby track plot, and enter the track -width (m), and track substrate, and indicate if the track -had been cleared prior (i.e. swept or dragged the day -before).
Select start nearby track plot . The app will record the -date, time, and location.
The optional nearby transect track survey option will only be +displayed in the app if it was selected during the survey set-up stage +(see above). This optional survey component should only be completed if +a suitable section of the nearby vehicle track occurs within 200 m of +the plot just surveyed, and if it safe to survey (i.e., no expected +vehicles).
+Navigate to the start of the transect.
Record the transect start location.
Enter the track width (m). This will also enable the app +to record the area searched by multiplying the track width by 100 +m.
Select the track substrate from the drop-down (sand, +gravel, mud) or input a custom value.
Indicate if the track had been cleared prior to survey +(i.e., swept or dragged the day before).
Select start transect. The app will automatically record +the survey start time.
Traverse 100 m of the track, zig-zagging side-to side. The app -will record the gps location every minute.
For each sign observed, select add sign record:
For each animal track observed, select add track and +record:
Location –the location of the observation is +automatically recorded when add sign is selected. Update if +required.
Date – the date and time of the +observation is automatically recorded when add sign is +selected. Update if required.
select the sign type (all options are available, despite -tracks and scats the only records that would be expected)
select the attributable fauna species (select -unknown if not certain)
indicate the sign age (fresh 1-2 days, old 3-7 days, -very old 7+ days) (optional field)
indicate the age class of the individual responsible for -the sign (optional field applicable to scats and tracks only based on -size)
add photo (representative photos should be taken for -each species/sign type for the plot – i.e. not all signs observed need -to be photographed, ideally a scale card should be used in all photos -(optional, up to 3 photos per sign record)
if warrens, burrows or dens are observed, count and record the -number of entrances and record if any are considered -active or not active (optional)
add any additional comments in the observation comments -field. Recording the gait length and width may be of interest, -particularly of feral cats and foxes to assist distinguishing -individuals.
Attributable fauna species – select from the drop-down +(cat, fox, wild dog, rabbit, deer species, goat, pig, horse, camel, +unknown) or input a custom value.
Age class – record if the attributable species is a +juvenile or adult (optional field).
+Number of individuals – record if multiple individuals can +be confidently discerned.
Add a representative photo of the track, particularly if +the attributable fauna species is unknown or observer confidence in +identification is low. A scale card should be used in all photos. +(optional field).
Add any comments. Recording the gait length and width +may be of interest, particularly of feral cats and foxes to assist +distinguishing individuals.
When you have reached the end of the track plot (100 m), select, -end track plot to record the end location to enable the app to -record the area searched.
When you have reached the end of the transect (100 m), select, +end transect. The transect end location and survey end time +will be recorded automatically.
Queue the collection for submission.
If conducting a repeated measure within the current visit, repeat +the entire process and create a new collection.
Pre-requisites for completing this protocol:
+None.
Survey activity time estimates will vary depending on the area to be surveyed, number and variety of signs encountered, number of measures @@ -42,7 +45,7 @@ practising, using field reference guides, and seeking advice before attempting to conduct this protocol.
Track stations do not involve interference with wildlife, and therefore scientific permits and wildlife ethics approvals are unlikely -to be required, but remember to always check with your local authority. +to be required but remember to always check with your local authority. Access permissions are required.
Surveys should only be conducted in good weather conditions, when -temperature, wind and rainfall are typical for the season. Poor weather -conditions will impact both animal movement, and chance of detection -through tracking. If conditions are less than optimal conditions, such -as significantly cooler/hotter/windier/wetter than expected, the survey -should be rescheduled. Wind is a particularly important factor when -detecting tracks of animals in sandy environments, therefore if it is -windier than a fresh wind (Beaufort scale 5, when small trees begin to -sway) the morning of the survey, consider rescheduling.
Conduct a reconnaissance field survey to identify which potential +survey sites (and any others sites not identified during pre-survey +planning) are suitable track station locations. Ensure habitats are +representative of the project area.
For each proposed track station, check that the location is +accessible in all weather conditions. Ensure that the substrate is +suitable for fauna to leave tracks. Identify any safety +hazards.
Travel to a track station location to begin a track station and +survey set-up. Using a broom, sweep the track station area clear of +tracks, sticks and leaf litter.
If using an external GNSS/GPS, ensure it is turned on and +connected to the mobile/tablet.
Open the Monitor app and select the Sign-based Fauna Survey +Module and then the Track station protocol.
Select create new track station to assign a new +track station ID. If conducting a repeated measure of an +established track station, select existing track station and +select the relevant track station ID from the dropdown, then +skip to step 7.
Record the track station information, including:
There is no rule for when to repeat surveys. Surveys should be -conducted as often as the project requires, i.e. weekly, monthly, -bi-monthly, quarterly. For consistency, aim to replicate the conditions, -i.e. similar weather, similar time, moon phase, observers, and reference -materials.
Location – recorded automatically. Update if +required.
Date – the date and time that the +track station is established is automatically recorded. Update if +required.
Track station width (cm) –record the width between 30 cm +and 200 cm.
Track station length (cm) – record the length between 30 +cm and 200 cm.
Track station substrate – select from dropdown (sand, +gravel, tracking plate, tracking pad) or input a custom value.
Track station downward photo – take a downward photo of +track station, holding the device in front of you looking directly down +to the station.
Track station spacing (m) – distance between track +stations (optional, can be updated using spatial data if +required).
Micro-habitat – select the micro-habitat that +best describes the immediate vicinity, i.e., within 1 m (open area, +under tree, under shrub, along animal pathway).
Micro-habitat photo – take a track station micro-habitat +photo, ideally whilst holding the device about 40 cm from the ground, +looking along from intended animal approach route.
Habitat (Major Vegetation Group) – select the Major +Vegetation Group that best represents the area. This is an optional +field and should be completed if no monitoring plots or mapped locations +using the Vegetation Mapping Module have been completed along or in the +vicinity of the track station.
Add any comments about the track station (e.g., the +presence of any palatable browse species or fauna refuge).
Save the track station. Additional track stations can be added by +selecting the add button (if the workflow involves setting up all track +stations prior to conducting surveys.
Record the survey information:
Observers should remain consistent throughout the duration of the +
Survey set-up ID – select create new survey +set-up and select the relevant track station ID to assign +a new survey set-up ID (track station ID-date).
Survey intent – indicate if survey intent is once-off +measure, repeated measure, linked to a pre-control activity or +post-control activity (optional).
Target species – select the target species (e.g., Cat, +Fox, Wild dog, Rabbit, Deer species, Goat, Pig, Horse, Camel). Select +‘Other’ to specify a species not in the dropdown. Multiple species can +be selected/specified.
Observer details – enter details for each observer, +including the observer name and observer role +(spotter, data entry). Multiple roles can be selected for each +observer.
Weather conditions – enter details of the +temperature, rainfall, duration of rainfall, +cloud cover, wind description, and moon phase. Note +the weather conditions can be adjusted at the completion of the survey.
Surveys should be conducted for a minimum of 3 consecutive days -(Cowled and Lapidge 2004, Mitchell and Balogh 2007b).
Where the species cannot be determined, provide as much -information as possible (e.g., carnivore, herbivore, hoofed, deer, -etc.). Remember to take representative photos of the signs.
Save the survey information. Survey information for additional +transects can be added by selecting the add button (if the workflow +involves setting up all surveys prior to conducting surveys.
Indicate when all track stations have been set, by completing the +track station set-up component. Follow the conduct the survey steps +below the next morning.
Return to a track station the morning after it was set-up to +conduct a survey.
Select the survey set-up ID based on the +relevant track station ID and associated survey +set-up.
If a track is observed, check the tracks observed +checkbox and record the following for each track encountered:
Weather conditions should be recorded at least once per day, but -can be recorded multiple times, if weather conditions change.
If you are not using a weather station or temperature gauge, use -the Bureau of Meteorology website (or other weather apps) to estimate -the temperature at the time of the survey for the closest weather -station (data can be checked with the closest weather station after the -survey if needed).
Moon phase is recorded as it plays an important role in how -bright the night sky is, and therefore can impact animal activity and -movement. Either observe the moon or use the Bureau of Meteorology -website (or other weather apps) to determine the moon phase for the date -of the survey.
Date – the date and time of the +observation is automatically recorded when add track is +selected. Update if required.
Attributable fauna species – select from the drop-down +(cat, fox, wild dog, rabbit, deer species, goat, pig, horse, camel, +unknown) or input a custom value.
Age class – record if the attributable species is a +juvenile or adult (optional field).
Number of individuals – record if multiple individuals +can be confidently discerned.
Add a representative photo of the track, particularly if +the attributable fauna species is unknown or observer confidence in +identification is low. A scale card should be used in all photos. +(optional field).
Add any comments.
Tracks are generally easiest to identify where the ground is soft -enough to allow imprinting, including muddy or sandy sites, such as -creek and dam banks, claypans, beaches and dried puddles, as well as -roadside dust (Triggs 1996).
The best tracks are found early in the morning and are easiest to -observe with the shadow behind the observer (Triggs 1996, Moseby et al. -2009).
Walk into the sun when recording tracks to optimise shadows (Arid -Zone Monitoring 2021).
Don’t depend on a single print for identification of a species, -look at multiple gaits of an animal and follow it until you are certain -of your identification (Southgate and Moseby 2008).
Save the track observation. Additional observations can be added +by selecting the add button.
Once all observations have been entered, save the track station +data.
Additional track stations can be surveyed by selecting the add +button.
Once all track stations have been completed, complete the track +station survey component.
Queue the collection for submission.
If conducting repeated measures within the current visit, repeat +the entire process and create a new collection, selecting from existing +track stations in the track station and survey set-up step.
Appendix 1. Data -collection fields from the Signs-based Fauna Survey Module
Complete lists are provided in the Monitor app, as well as the TERN -website
+website.Transect route type | +Route type |
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Survey intent | +Survey intent |
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Target species | +Target species |
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Survey type | +Tracking substrate |
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Observer role | +Track station substrate |
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Micro-habitat | +|
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Weather conditions | +Habitat (Major Vegetation Group) |
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Observer role | +|
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Sign type* (not a complete list) | +Weather conditions |
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NVIS Major Vegetation Group | -NVIS Major Vegetation Sub-group | -|
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Rainforest and Vine Thickets (MVG 1) | -Cool temperate rainforest | +
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Tropical or sub-tropical rainforests | +
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Dry rainforest | +
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Vine thickets | +
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Eucalypt Tall Open Forests (MVG 2) | -Eucalyptus tall open forests with a dense broad-leaved and/or -tree-fern understorey (wet-sclerophyll) | +
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Eucalyptus tall open forests with a fine-leaved shrubby understorey -OR Eucalyptus tall open forests and open forests with ferns, herbs, -sedges, rushes or wet tussock grasses | +
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Eucalypt Open Forests (MVG 3) | -Eucalyptus open forests with a shrubby understorey | +
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Eucalyptus open forests with a grassy understorey | +
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Eucalypt Low Open Forests (MVG 4) | -- | +
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Eucalypt Woodlands (MVG 5) | -Eucalyptus woodlands with a shrubby understorey OR Eucalyptus -woodlands with a chenopod or samphire understorey | +
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Eucalyptus woodlands with a grassy understorey OR Eucalyptus -woodlands with ferns, herbs, sedges, rushes or wet tussock grassland OR -Eucalyptus woodlands with a hummock grass understorey | +
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Acacia Forests and Woodlands (MVG 6) | -Brigalow (Acacia harpophylla) forests and woodlands | +
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Other Acacia forests and woodlands | +
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Mulga (Acacia aneura) woodlands and shrublands +/- tussock -grass +/- forbs OR Mulga (Acacia aneura) woodlands and -shrublands with hummock grass | +
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Callitris Forests and Woodlands (MVG 7) | -Callitris forests and woodlands (Eastern occurrence) | +
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Callitris forests and woodlands (mallee, arid and semi-arid -occurrence) | +
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Casuarina Forests and Woodlands (MVG 8) | -Casuarina and Allocasuarina forests and woodlands | +
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River Oak forests and woodlands | +
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Melaleuca Forests and Woodlands (MVG 9) | -Melaleuca open forests and woodlands | +
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Other Forests and Woodlands (MVG 10) | -Other forests and woodlands OR Banksia woodlands OR Leptospermum -forests and woodlands OR Tropical mixed species forests and -woodlands | +
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Eucalypt Open Woodlands (MVG 11) | -Eucalyptus open woodlands with a grassy understorey OR Eucalyptus -open woodlands with shrubby understorey | +
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Eucalyptus low open woodlands with tussock grass OR Eucalyptus low -open woodlands with a shrubby understorey OR Eucalyptus low open -woodlands with a chenopod or samphire understorey | +
Plot type | ||
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Tropical Eucalypt Woodlands / Grasslands (MVG 12) | -Tropical Eucalyptus forests and woodlands with a tall annual grassy -understorey | +
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Acacia Open Woodlands (MVG 13) | -Mulga (Acacia aneura) open woodlands and sparse shrublands -+/- tussock grass OR Mulga (Acacia aneura) open woodlands and -sparse shrublands with hummock grass | +
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+
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Corner start point | ||
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Mallee Woodlands and Shrublands (MVG 14) | -Mallee with hummock grass OR Mallee with a tussock grass understorey -OR Mallee with a dense shrubby understorey OR Mallee with an open -shrubby understorey | +
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Low Closed Forest and Tall Closed Shrublands (MVG 15) | -Low closed forests or tall closed shrublands (including Acacia, -Melaleuca and Banksia) | +
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Acacia shrublands (MVG 16) | -Acacia (+/- low) open woodlands and sparse shrublands with a shrubby -understorey OR Acacia (+/- low) open woodlands and sparse shrublands -with hummock grass OR Acacia (+/- low) open woodlands and sparse -shrublands with tussock grass OR Acacia (+/- low) open woodlands and -sparse shrublands with chenopods. | +
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Other Acacia tall open shrublands and shrublands | +
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+
Sign type | ||
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Other Shrublands (MVG 17) | -Melaleuca shrublands and open shrublands OR Casuarina/Allocasuarina -shrublands (C. equisetifolia, A. littoralis, -A. verticillata) OR other shrublands | +
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Lignum shrublands and wetlands | +
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Heathlands (MVG 18) | -Heathlands | +
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Tussock Grasslands (MVG 19) | -Temperate tussock grassland | +
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Mitchell grass (Astrebla) tussock grasslands and Blue grass -(Dichanthium) and tall bunch grass (Chrysopogon) -tussock grasslands OR Other tussock grasslands | +
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Hummock Grasslands (MVG 20) | -Hummock grasslands | +
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Other Grasslands, Herblands, Sedgelands and Rushlands -(MVG 21) | -Sedgelands, rushes or reeds OR Wet tussock grasslands with herbs, -sedges or rushes, herblands or ferns OR Other grasslands | +
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Saline or brackish sedgelands or grasslands | +
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Chenopod Shrublands, Samphire Shrublands and Forblands -(MVG 22) | -Saltbush and/or Bluebush shrublands | +
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Mixed chenopod, samphire +/- forbs | +
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Mangroves (MVG 23) | -Mangroves (Northern) | +
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Mangroves (Southern) | +
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+|
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+
Sign age | ||
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Other Open Woodlands (MVG 31) | -Callitris open woodlands OR Melaleuca open woodlands OR Other open -woodlands | +
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Casuarina and Allocasuarina open woodlands with a shrubby -understorey OR Casuarina and Allocasuarina open woodlands with a -chenopod shrub understorey OR Casuarina and Allocasuarina open woodlands -with a tussock grass understorey OR Casuarina and Allocasuarina open -woodlands with a hummock grass understorey | +
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+|
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Age class | ||
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Mallee Open Woodlands and Sparse Mallee Shrublands (MVG 32) | -Open mallee woodlands and sparse mallee shrublands with a dense -shrubby understorey OR Open mallee woodlands and sparse mallee -shrublands with a sparse shrubby understorey OR Open mallee woodlands -and sparse mallee shrublands with a tussock grass understorey OR Open -mallee woodlands and sparse mallee shrublands with a hummock grass -understorey | +
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+
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Mobile device (tablet/phone capable of taking high resolution -photos) with the app (progressive web app) saved to the home -screen
GNSS such as a Trimble R1 or DA2 receiver, a hand-held GPS or -device built-in GPS (least preferred), capable of achieving <30 cm -accuracy
Mobile device (tablet/phone) with the Monitor app +installed
GNSS receiver capable of achieving <30 cm accuracy (e.g., +Trimble R1 or DA2), hand-held GPS, or device built-in GPS (least +preferred)
Field guide or other resources for identification of tracks
Hand lens
Sand or other suitable tracking surface
Rake/broom
Scale card
Camera.
Professional camera (optional).
Conduct a reconnaissance field survey to identify which potential +survey sites (and any others sites not identified during pre-survey +planning) are suitable track station locations. Ensure habitats are +representative of the project area.
For each proposed track station, check that the location is +accessible in all weather conditions. Ensure that the substrate is +suitable for fauna to leave tracks. Identify any safety +hazards.
Arrive at the survey location and assess the proposed track -station locations.
Travel to a track station location to begin a track station and +survey set-up. Using a broom, sweep the track station area clear of +tracks, sticks and leaf litter.
Check the station areas are free of vegetation, leaf litter, has -substrate is suitable for leaving tracks (i.e., sand or light gravel) or -is suitable placement for a tracking pad or plate.
If using an external GNSS/GPS, ensure it is turned on and connected to the mobile/tablet.
Open the Monitor app and select Sign-based Fauna Survey -Module > Vehicle tracks and track station protocol.
Select either an existing track station and choose the -applicable track station identification code from the drop-down list, or -select create new track station to assign a new track station -identification.
Enter the dominant NVIS Major Vegetation Group that best -represents the area (see Appendix 1). This optional field should be completed if no other -monitoring plots or mapped locations using the Vegetation Mapping Module -have been completed along or near the transect.
Select the track station micro-habitat that best -describes the immediate vicinity (i.e. within 1 m) (open area, under -tree, under shrub, along animal pathway), and add any key comments -(include presence of any palatable browse species, fauna refuge presence -etc).
Indicate if the survey intent is a once-off measure, -repeated measure, linked to a pre-control activity or post-control -activity (optional).
Enter the track station width and track station -length (each between 30 cm and 200 cm).
Enter the track station substrate (sand, gravel, -tracking plate, tracking pad).
Using a broom, sweep the track station area clear of tracks, -sticks and leaf litter.
Take a track station downward photo, holding the device -in front of you looking directly down to the station.
Take a track station micro-habitat photo, ideally whilst -holding the device about 40 cm from the ground, looking along from -intended animal approach route.
Select track station set. The app will record the -location, date and time.
Traverse to the next track station, and select, add track -station, and repeat the process for each additional track station -being established.
Indicate when all track stations have been set, by selecting -track station set-up complete.
Open the Monitor app and select the Sign-based Fauna Survey +Module and then the Track station protocol.
Select create new track station to assign a new +track station ID. If conducting a repeated measure of an +established track station, select existing track station and +select the relevant track station ID from the dropdown, then +skip to step 7.
Record the track station information, including:
Location – recorded automatically. Update if +required.
Date – the date and time that the +track station is established is automatically recorded. Update if +required.
Track station width (cm) –record the width between 30 cm +and 200 cm.
Track station length (cm) – record the length between 30 +cm and 200 cm.
Track station substrate – select from dropdown (sand, +gravel, tracking plate, tracking pad) or input a custom value.
Track station downward photo – take a downward photo of +track station, holding the device in front of you looking directly down +to the station.
Track station spacing (m) – distance between track +stations (optional, can be updated using spatial data if +required).
Micro-habitat – select the micro-habitat that +best describes the immediate vicinity, i.e., within 1 m (open area, +under tree, under shrub, along animal pathway).
Micro-habitat photo – take a track station micro-habitat +photo, ideally whilst holding the device about 40 cm from the ground, +looking along from intended animal approach route.
Habitat (Major Vegetation Group) – select the Major +Vegetation Group that best represents the area. This is an optional +field and should be completed if no monitoring plots or mapped locations +using the Vegetation Mapping Module have been completed along or in the +vicinity of the track station.
Add any comments about the track station (e.g., the +presence of any palatable browse species or fauna refuge).
Save the track station. Additional track stations can be added by +selecting the add button (if the workflow involves setting up all track +stations prior to conducting surveys.
Record the survey information:
Survey set-up ID – select create new survey +set-up and select the relevant track station ID to assign +a new survey set-up ID (track station ID-date).
Survey intent – indicate if survey intent is once-off +measure, repeated measure, linked to a pre-control activity or +post-control activity (optional).
Target species – select the target species (e.g., Cat, +Fox, Wild dog, Rabbit, Deer species, Goat, Pig, Horse, Camel). Select +‘Other’ to specify a species not in the dropdown. Multiple species can +be selected/specified.
Observer details – enter details for each observer, +including the observer name and observer role +(spotter, data entry). Multiple roles can be selected for each +observer.
Weather conditions – enter details of the +temperature, rainfall, duration of rainfall, +cloud cover, wind description, and moon phase. Note +the weather conditions can be adjusted at the completion of the +survey.
Save the survey information. Survey information for additional +transects can be added by selecting the add button (if the workflow +involves setting up all surveys prior to conducting surveys.
Indicate when all track stations have been set, by completing the +track station set-up component. Follow the conduct the survey steps +below the next morning.
Once the survey details have been entered, the app will bring up -the field survey screen, which is populated according to the information -previously entered. Ensure that the correct Plot/station ID is -selected in the app.
Complete the weather details fields, and consider the -conditions of the previous 24 hours, not just the present -conditions.
Move to the first station and record all tracks -encountered.
Return to a track station the morning after it was set-up to +conduct a survey.
Select the survey set-up ID based on the +relevant track station ID and associated survey +set-up.
If a track is observed, check the tracks observed +checkbox and record the following for each track encountered:
For each track record the species and observer -confidence.
If the number of individuals can be identified, this should be -recorded.
If species ID is approximate, undetermined or if observer -confidence is low, a picture should be taken. Notes about tracks -observed can be recorded in the free text field (optional).
If no tracks are present, select No tracks.
Date – the date and time of the +observation is automatically recorded when add track is +selected. Update if required.
Attributable fauna species – select from the drop-down +(cat, fox, wild dog, rabbit, deer species, goat, pig, horse, camel, +unknown) or input a custom value.
Age class – record if the attributable species is a +juvenile or adult (optional field).
Number of individuals – record if multiple individuals +can be confidently discerned.
Add a representative photo of the track, particularly if +the attributable fauna species is unknown or observer confidence in +identification is low. A scale card should be used in all photos. +(optional field).
Add any comments.
Once all observations have been entered, save the data and if the -survey will be repeated again the following morning, prepare the plot -surface, and record in the app that this has been completed. Ensure that -data on each consecutive day is collected against the appropriate -transect ID.
Repeat step 2 until all stations have been surveyed.
To complete the survey when all stations have been surveyed -across all days, select End survey.
Select the Save icon to return to the survey screen and -select the Home icon to return to the home page.
Save the track observation. Additional observations can be added +by selecting the add button.
Once all observations have been entered, save the track station +data.
Additional track stations can be surveyed by selecting the add +button.
Once all track stations have been completed, complete the track +station survey component.
Queue the collection for submission.
If conducting repeated measures within the current visit, repeat +the entire process and create a new collection, selecting from existing +track stations in the track station and survey set-up step.
Pre-requisites for completing this protocol:
+None.
Survey activity time estimates will vary depending on the area to be surveyed, number and variety of signs encountered, number of measures @@ -172,7 +175,7 @@ observation. Wildlife Research 28:151-164.
"""^^rdf:HTML ; skos:note """Surveys should only be conducted in good weather conditions, when temperature, wind and rainfall are typical for the season. Poor weather @@ -187,10 +190,10 @@ sway) the morning of the survey, consider rescheduling.
There is no rule for when to repeat surveys. Surveys should be -conducted as often as the project requires, i.e. weekly, monthly, +conducted as often as the project requires, i.e., weekly, monthly, bi-monthly, quarterly. For consistency, aim to replicate the conditions, -i.e. similar weather, similar time, moon phase, observers, and reference -materials.
Weather conditions should be recorded at least once per day, but can be recorded multiple times, if weather conditions change.
Appendix 1. Data -collection fields from the Signs-based Fauna Survey Module
Complete lists are provided in the Monitor app, as well as the TERN -website
+website.Transect route type | +Route type |
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Survey intent | +Survey intent |
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Target species | +Target species |
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Survey type | +Tracking substrate |
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Observer role | +Track station substrate |
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Micro-habitat | +|
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Weather conditions | +Habitat (Major Vegetation Group) |
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Observer role | +|
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Sign type* (not a complete list) | +Weather conditions |
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NVIS Major Vegetation Group | -NVIS Major Vegetation Sub-group | -|
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+||
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Rainforest and Vine Thickets (MVG 1) | -Cool temperate rainforest | +
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Tropical or sub-tropical rainforests | +
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Dry rainforest | +
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Vine thickets | +
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Eucalypt Tall Open Forests (MVG 2) | -Eucalyptus tall open forests with a dense broad-leaved and/or -tree-fern understorey (wet-sclerophyll) | +
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Eucalyptus tall open forests with a fine-leaved shrubby understorey -OR Eucalyptus tall open forests and open forests with ferns, herbs, -sedges, rushes or wet tussock grasses | +
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Eucalypt Open Forests (MVG 3) | -Eucalyptus open forests with a shrubby understorey | +
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Eucalyptus open forests with a grassy understorey | +
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Eucalypt Low Open Forests (MVG 4) | -- | +
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Eucalypt Woodlands (MVG 5) | -Eucalyptus woodlands with a shrubby understorey OR Eucalyptus -woodlands with a chenopod or samphire understorey | +
|
Eucalyptus woodlands with a grassy understorey OR Eucalyptus -woodlands with ferns, herbs, sedges, rushes or wet tussock grassland OR -Eucalyptus woodlands with a hummock grass understorey | +
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Acacia Forests and Woodlands (MVG 6) | -Brigalow (Acacia harpophylla) forests and woodlands | +
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Other Acacia forests and woodlands | +
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Mulga (Acacia aneura) woodlands and shrublands +/- tussock -grass +/- forbs OR Mulga (Acacia aneura) woodlands and -shrublands with hummock grass | +
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Callitris Forests and Woodlands (MVG 7) | -Callitris forests and woodlands (Eastern occurrence) | +
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Callitris forests and woodlands (mallee, arid and semi-arid -occurrence) | +
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Casuarina Forests and Woodlands (MVG 8) | -Casuarina and Allocasuarina forests and woodlands | +
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River Oak forests and woodlands | +
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Melaleuca Forests and Woodlands (MVG 9) | -Melaleuca open forests and woodlands | +
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Other Forests and Woodlands (MVG 10) | -Other forests and woodlands OR Banksia woodlands OR Leptospermum -forests and woodlands OR Tropical mixed species forests and -woodlands | +
|
Eucalypt Open Woodlands (MVG 11) | -Eucalyptus open woodlands with a grassy understorey OR Eucalyptus -open woodlands with shrubby understorey | +
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Eucalyptus low open woodlands with tussock grass OR Eucalyptus low -open woodlands with a shrubby understorey OR Eucalyptus low open -woodlands with a chenopod or samphire understorey | +
Plot type | ||
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Tropical Eucalypt Woodlands / Grasslands (MVG 12) | -Tropical Eucalyptus forests and woodlands with a tall annual grassy -understorey | +
|
Acacia Open Woodlands (MVG 13) | -Mulga (Acacia aneura) open woodlands and sparse shrublands -+/- tussock grass OR Mulga (Acacia aneura) open woodlands and -sparse shrublands with hummock grass | +
|
Mallee Woodlands and Shrublands (MVG 14) | -Mallee with hummock grass OR Mallee with a tussock grass understorey -OR Mallee with a dense shrubby understorey OR Mallee with an open -shrubby understorey | +
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+
Corner start point | +||
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Low Closed Forest and Tall Closed Shrublands (MVG 15) | -Low closed forests or tall closed shrublands (including Acacia, -Melaleuca and Banksia) | +
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Acacia shrublands (MVG 16) | -Acacia (+/- low) open woodlands and sparse shrublands with a shrubby -understorey OR Acacia (+/- low) open woodlands and sparse shrublands -with hummock grass OR Acacia (+/- low) open woodlands and sparse -shrublands with tussock grass OR Acacia (+/- low) open woodlands and -sparse shrublands with chenopods. | +
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Other Acacia tall open shrublands and shrublands | +
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+
Sign type | ||
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Other Shrublands (MVG 17) | -Melaleuca shrublands and open shrublands OR Casuarina/Allocasuarina -shrublands (C. equisetifolia, A. littoralis, -A. verticillata) OR other shrublands | +
|
Lignum shrublands and wetlands | +
|
|
Heathlands (MVG 18) | -Heathlands | +
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Tussock Grasslands (MVG 19) | -Temperate tussock grassland | +
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Mitchell grass (Astrebla) tussock grasslands and Blue grass -(Dichanthium) and tall bunch grass (Chrysopogon) -tussock grasslands OR Other tussock grasslands | +
|
|
Hummock Grasslands (MVG 20) | -Hummock grasslands | +
|
Other Grasslands, Herblands, Sedgelands and Rushlands -(MVG 21) | -Sedgelands, rushes or reeds OR Wet tussock grasslands with herbs, -sedges or rushes, herblands or ferns OR Other grasslands | +
|
Saline or brackish sedgelands or grasslands | +
|
|
Chenopod Shrublands, Samphire Shrublands and Forblands -(MVG 22) | -Saltbush and/or Bluebush shrublands | +
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Mixed chenopod, samphire +/- forbs | +
|
|
Mangroves (MVG 23) | -Mangroves (Northern) | +
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Mangroves (Southern) | +
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Other Open Woodlands (MVG 31) | -Callitris open woodlands OR Melaleuca open woodlands OR Other open -woodlands | +
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+
Sign age | +||
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Casuarina and Allocasuarina open woodlands with a shrubby -understorey OR Casuarina and Allocasuarina open woodlands with a -chenopod shrub understorey OR Casuarina and Allocasuarina open woodlands -with a tussock grass understorey OR Casuarina and Allocasuarina open -woodlands with a hummock grass understorey | +
|
|
Mallee Open Woodlands and Sparse Mallee Shrublands (MVG 32) | -Open mallee woodlands and sparse mallee shrublands with a dense -shrubby understorey OR Open mallee woodlands and sparse mallee -shrublands with a sparse shrubby understorey OR Open mallee woodlands -and sparse mallee shrublands with a tussock grass understorey OR Open -mallee woodlands and sparse mallee shrublands with a hummock grass -understorey | +
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+
Age class | +
---|
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+
|
Mobile device (tablet/phone capable of taking high resolution -photos) with the app (progressive web app) saved to the home -screen
GNSS such as a Trimble R1 or DA2 receiver, a hand-held GPS or -device built-in GPS (least preferred), capable of achieving <30 cm -accuracy
Mobile device (tablet/phone) with the Monitor app +installed
GNSS receiver capable of achieving <30 cm accuracy (e.g., +Trimble R1 or DA2), hand-held GPS, or device built-in GPS (least +preferred)
Field guide or other resources for identification of tracks
Hand lens
Iron drag or equivalent
4WD vehicle or other suitable vehicle
Scale card
Professional camera (optional).
Arrive at the locations that have been pre-determined. Check the -route of vehicle tracks and ensure the length is suitable for clearing -of tracks by dragging a heavy object behind a vehicle, and that the -substrate is suitable for leaving tracks. Avoid sections of hard gravel. -Identify any safety hazards. If necessary, amend the transect start -location, route and end location.
Conduct a reconnaissance field survey to identify which potential +survey sites (and any others sites not identified during pre-survey +planning) are suitable transect locations. Ensure habitats are +representative of the project area.
Open the Monitor app and select Sign-based Fauna Survey -Module > Vehicle tracks protocol.
Select either an existing transect and choose the -applicable transect ID code from the drop-down list, or select -create new transect to assign a new transect code.
Enter the dominant NVIS Major Vegetation Group that best -represents the transect (see Appendix 1). This optional field should be completed if no -other monitoring plots or mapped locations using the Vegetation Mapping -Module have been completed along or near the transect. See the -Vegetation Mapping Module for further information.
Indicate if the survey intent is a once-off measure, repeated -measure, linked to a pre-control activity or post-control activity -(optional).
Enter the transect route type that best represents the -transect (vehicle dirt track, or enter an alternative in the free text -field).
Clear the vehicle track using an iron drag attached to a 4WD or -equivalent.
For each proposed transect, check the route and ensure the entire +length is traversable in all weather conditions. Ideally, transects +should be a straight line but vehicle tracks may meander slightly. +Ensure the width and length of the route is suitable for clearing of +tracks by dragging a heavy object behind a vehicle, and that the +substrate is suitable for fauna to leave tracks. Avoid sections of hard +gravel. Identify the best direction of travel and any safety +hazards.
Determine the transect start locations, routes and end +locations.
Travel to a transect start location to begin a transect and +survey set-up.
If using an external GNSS/GPS, ensure it is turned on and +connected to the mobile/tablet.
Open the Monitor app and select the Sign-based Fauna Survey +Module and then the Vehicle track protocol.
Select create new transect to assign a new transect +ID. If conducting a repeated measure of an established transect, +select existing transect and select the relevant transect +ID from the dropdown, then skip to step 7.
Record the transect information, including:
Enter the track width (between 2 and 10 m).
Enter the track substrate (sand, gravel etc).
Transect Start Location – recorded automatically. Update +if required.
Date – the date and time that the +transect is established is automatically recorded. Update if +required.
Route type – select a value that best represents the +transect from the dropdown (vehicle road, vehicle dirt track) or input a +custom value.
Transect alignment (°) – based on the direction of +travel. If the transect meanders with the vehicle track, consider the +overall direction of travel.
Transect width (m) – record the width of the vehicle +track.
Transect length (m) – record the length of the of the +transect.
Transect spacing (m) – distance between transects +(optional, can be updated using spatial data if required).
Habitat (Major Vegetation Group) – select the Major +Vegetation Group that best represents the transect. This is an optional +field and should be completed if no monitoring plots or mapped locations +using the Vegetation Mapping Module have been completed along or in the +vicinity of the transect.
Select start track drag, and commence driving. Drive at -a speed suitable for clearing the track under the conditions. The app -will record the start location, date and time, and the route -taken.
When you reach the end of the track section you plan to survey, -select end track drag. The app will record the location, date -and time.
Save the transect. Additional transects can be added by selecting +the add button (if the workflow involves setting up all transects prior +to conducting surveys.
Record the survey information:
Survey set-up ID – select create new survey +set-up and select the relevant transect ID to assign a new +survey set-up ID (transect ID-date).
Survey intent – indicate if survey intent is once-off +measure, repeated measure, linked to a pre-control activity or +post-control activity (optional).
Target species – select the target species (e.g., Cat, +Fox, Wild dog, Rabbit, Deer species, Goat, Pig, Horse, Camel). Select +‘Other’ to specify a species not in the dropdown. Multiple species can +be selected/specified.
Tracking substrate – record the tracking +substrate at the time of the survey from the drop-down (sand, +gravel, mud) or input a custom value.
Tracking width (m) – record the width of the vehicle +track that will be cleared to prepare a blank tracking +substrate.
Observer details – enter details for each observer, +including the observer name and observer role +(spotter, data entry). Multiple roles can be selected for each +observer.
Weather conditions – enter details of the +temperature, rainfall, duration of rainfall, +cloud cover, wind description, and moon phase. Note +the weather conditions can be adjusted at the completion of the +survey.
Clear the vehicle track using an iron drag attaced to a 4WD or +equivalent. Select start track drag, and commence driving. +Drive at a speed suitable for clearing the track under the conditions. +The app will record the start location, date and +time, and the route taken.
When the end of the track section to be surveyed is reached, +select end track drag. The app will record the end +location, date and time.
Save the survey information. Survey information for additional +transects can be added by selecting the add button (if the workflow +involves setting up all surveys prior to conducting surveys.
Complete the survey set-up component and follow the conduct the +survey steps below the next morning.
Return to a transect start location the morning after the +transect was cleared to a conduct a survey.
Select the survey set-up ID based on the +relevant transect ID and associated survey set-up. If +conducting a repeated measure, ensure the survey set-up ID +aligns with the existing measure/s.
Select start transect. The app will record the start +location, date and time, and begin the track +log.
+Walk the length of transect. If a track is observed, check the +tracks observed checkbox and record the following for each +track encountered:
Once the survey details have been entered, the app will bring up -the field survey screen, which is populated according to the information -previously entered.
Select the transect ID (drop-down list) or manually -enter using a unique ID in the Transect ID text box. If -undertaking a repeat survey, ensure the correct ID has been selected (if -required, refer to the mapping interface to check plot -locations).
Complete the weather details fields, and consider the -conditions of the previous 24 hours, not just the present -conditions.
Select Start transect, to automatically record start -time/date and to begin the track log. You can pause the survey at any -point and all details entered will be saved to be returned to later -using the pause button.
Record all tracks that are encountered.
For each track record the species and observer -confidence.
If the number of individuals is known, this should be -recorded.
If species ID is approximate, undetermined or if observer -confidence is low, a picture should be taken Notes about tracks observed -can be recorded in the free text field (optional).
If no tracks are present select No tracks.
Location –the location of the observation is +automatically recorded when add track is selected. Update if +required.
Date – the date and time of the +observation is automatically recorded when add track is +selected. Update if required.
Attributable fauna species – select from the drop-down +(cat, fox, wild dog, rabbit, deer species, goat, pig, horse, camel, +unknown) or input a custom value.
Age class – record if the attributable species is a +juvenile or adult (optional field).
Number of individuals – record if multiple individuals +can be confidently discerned.
Add a representative photo of the track, particularly if +the attributable fauna species is unknown or observer confidence in +identification is low. A scale card should be used in all photos. +(optional field).
Add any comments. Recording the gait length and width +may be of interest, particularly of feral cats and foxes to assist +distinguishing individuals.
At the end of the transect select End transect to -complete the track count. Location and time will be automatically -recorded.
Ensure that you clear the transect of tracks for the survey to be -repeated the following morning. This can be done using an iron drag or -rake depending on the size of the transect. Ensure that data on each -consecutive day is collected against the appropriate transect -ID.
To complete the survey when all transects have been traversed -select End survey
Select the Save icon to return to the survey screen and -select the Home icon to return to the home page.
Save the track observation. Additional observations can be added +by selecting the add button.
At the end of the transect, select end transect to +complete the survey. The app will record the end location, +date and time.
Additional transects can be surveyed by selecting the add +button.
Once all transects have been completed, complete the transect +survey component.
Queue the collection for submission.
If conducting repeated measures within the current visit, repeat +the entire process and create a new collection, selecting from existing +transects in the transect and survey set-up step.
Pre-requisites for completing this protocol:
The plot must be established using the Plot Selection and Layout -Module prior to the conducting the Within-plot belt transect +
The plot must be established using the Plot Selection and Layout +Module prior to the conducting the Within-plot belt transect protocol.
The Plot Description Module must be completed prior to, or during -the reconnaissance visit.
Survey activity time estimates will vary depending on the number and @@ -44,7 +41,7 @@ varies depending on the frequency and variety of signs, the number of measures recorded, and if scats are being collected and removed or only recorded.
Personnel number and skills:
Within-plot belt transects are best conducted with two personnel, @@ -96,7 +93,7 @@ spatial patterns of defecation in wild boar. Wildlife Society Bulletin M. N. Gentle, L. J. McLeod, P. D. Meek, and G. R. Saunders. 2014. Management of wild canids in Australia: free-ranging dogs and red foxes. Pages 105–149 in A. Glen and C. Dickman, editors. Carnivores of -Australia: Past, Present and Future. CSIRO Publishing, Collingwood, +Australia: past, present and future. CSIRO Publishing, Collingwood, Victoria.
Higashide, D., T. Kuriyama, S. Takagi, Y. Nakashima, K. Fukasawa, G. Yajima, M. Kasada, and M. Yokoyama. 2021. Effectiveness of signs of @@ -120,9 +117,6 @@ Energy. Department of the Environment and Energy, Canberra.
Kennedy, M., B. L. Phillips, S. Legge, S. A. Murphy, and R. A. Faulkner. 2012. Do dingoes suppress the activity of feral cats in northern Australia? Austral Ecology 37:134-139.
-Koichi, K., D. Holliday, and C. e. Harris. 2020. Glovebox Guide for -Managing Feral Pigs v2.0. PestSmart Toolkit publication., The Centre for -Invasive Species Solutions, Canberra ACT.
Masters, P., N. Markopoulos, B. Florance, and R. Southgate. 2018. The eradication of fallow deer (Dama dama) and feral goats (Capra hircus) from Kangaroo Island, South Australia. @@ -171,7 +165,7 @@ Network at WWF Australia, Sydney.
Backhouse, K. Bellchambers, R. Brandle, P. Brenton, and P. Copley. 2022. Designing a large‐scale track‐based monitoring program to detect changes in species distributions in arid Australia. Ecological -Applications:e2762. +applications:e2762.Threatened Species Recovery Hub. undated. Data collection in track-based surveys.
Triggs, B. 1996. Tracks, scats and other traces. A field guide to @@ -180,34 +174,18 @@ Australian mammals. Oxford University Press Australia, Melbourne.
estimate the abundance of terrestrial carnivores using field signs and observation. Wildlife Research 28:151-164."""^^rdf:HTML ; rdfs:isDefinedByThere is no limitation to the length of transects. However, -transect lengths are typically restricted to personnel resources, -logistics of completing the surveys, and the window of opportunity to -survey under the same weather conditions. As a guide, transects should -be a minimum of 1 km in length.
Optimal quadrat size depends on the terrain, substrate, -vegetation cover, and the number of pest signs being recorded per -quadrat, and for data recording ease, the number of observers searching -for signs. Assuming the quadrat is searched by one observer spotting the -signs and one person completing the data entry, the recommended width -should be 1-2 m and not exceed 4 m. It is recommended that one observer -walks on the outer edge (i.e. 4 m) from the transect tape, and walks -parallel to the tape and only looking for signs that are within the -quadrat, i.e. between them and the tape. The other person completing the -data entry should walk along the tape, reading the tape to identify the -end of each quadrat length. Quadrat length should be between 1 m and 20 -m.
There is no rule for when to repeat surveys. Surveys should be +conducted as often as the project requires, i.e., weekly, monthly, +bi-monthly, quarterly. For consistency, aim to replicate the conditions, +i.e., similar weather, similar time, moon phase, observers, and +reference materials.
Surveys should only be conducted in good weather conditions, when temperature, wind and rainfall are typical for the season. Poor weather @@ -219,15 +197,7 @@ detecting tracks of animals in sandy environments, therefore if it is windier than a fresh wind (Beaufort scale 5, when small trees begin to sway) the morning of the survey, consider rescheduling.
There is no rule for when to repeat surveys. Surveys should be -conducted as often as the project requires, i.e. weekly, monthly, -bi-monthly, quarterly. For consistency, aim to replicate the conditions, -i.e. similar weather, similar time, moon phase, observers, and reference -materials.
Observers should remain consistent throughout the duration of the survey.
Weather conditions should be recorded at least once per day, but can be recorded multiple times, if weather conditions change.
Tracks are generally easiest to identify where the ground is soft enough to allow imprinting, including muddy or sandy sites, such as @@ -267,29 +237,28 @@ Zone Monitoring 2021).
Scats can either be recorded as present/absent or counted within each quadrat (optional).
Scats can be left in situ or removed during the survey to allow for a faecal accumulation rate to be calculated on future surveys -(optional) (Engeman et al. 2013) (Engeman et al. 2013, Ferretti et al. -2015).
If scats are removed they should be picked up by hand (gloves are -recommended), bagged and moved away from the transect line or any other -transect lines that are being surveyed or may be surveyed in the future. -Scats can be moved to the outer edge of the plot away from other +(optional) (Engeman et al. 2013, Ferretti et al. 2015).
If scats are removed, they should be picked up by hand (gloves +are recommended), bagged and moved away from the transect line or any +other transect lines that are being surveyed or may be surveyed in the +future. Scats can be moved to the outer edge of the plot away from other transect lines. Do not create excessive disturbance by raking or sweeping the scats.
Warrens and dens are recorded as being present, and active or in-active entrances within each quadrat are recorded (optional). There -is no need to count the number of entrances in each quadrat, or note -each entrance's active or in-active status.
Active burrows have an entrance that is not blocked by spiderwebs or vegetation, usually with tracks, scrapings and/or scats at the entrance. Some animals have burrow systems with multiple entrances, some @@ -297,7 +266,7 @@ freshly used and others older, so if you find a burrow that looks unused, check nearby for active entrances (Threatened Species Recovery Hub undated).
Very fresh tracks on good tracking surfaces are usually very clear, with small features like claws and footpads visible. Check tracks @@ -313,17 +282,897 @@ smell.
Complete lists are provided in the Monitor app, as well as the TERN +website.
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General:
Mobile device with the Monitor app installed
GNSS, such as a Trimble R1 or DA2 receiver, a hand-held GPS or -device built-in GPS (least preferred), capable of achieving <30 cm -accuracy
Mobile device (tablet/phone) with the Monitor app +installed
GNSS receiver capable of achieving <30 cm accuracy (e.g., +Trimble R1 or DA2), hand-held GPS, or device built-in GPS (least +preferred)
Field guides for identifying signs to species level
Scale card
100 m tape measure
1 m pole or 5–10 m retractable tape measure.
1 m pole or pocket tape measure locked at 1 m.
For removal of scats for faecal accumulation rates:
Bags for scat removal and temporary storage.
Arrive at the plot prior to the intended survey date. Traverse -the plot to assess vegetation cover, density, and substrate. Assess the -surface condition to ensure areas of bare ground are present and the -entirity of the plot is not covered in vegetation or leaf -litter.
Traverse the plot to assess vegetation cover, density, and +substrate. Assess the surface condition to ensure areas of bare ground +are present and the entirity of the plot is not covered in vegetation or +leaf litter. Determine the number of transects that will be surveyed +given the survey design, and time permitted.
If using an external GNSS/GPS, ensure it is turned on and +connected to the mobile/tablet.
Ensure the Plot Selection and Layout Module has been completed to +define the current plot and visit in the Monitor app.
If the proposed location is deemed suitable, complete the Plot -Selection and Layout Module to mark out the plot boundary and define the -current visit in the Monitor app.
Complete the Standard protocol within the Plot Description Module.
Open the Monitor app and select Sign-based Fauna Survey -Module > Within-plot belt transects protocol.
Select the number of transects to be completed (1, 2 or -4) using the drop-down list. The app will pre-determine which transects -to complete based on the number selected.
Select survey intent using the drop-down (once-off -measure, repeated measure, linked to a pre-control activity or -post-control activity, other). If other is selected, record the intent -using the text box.
Select the target species (cat, fox, wild dog, rabbit, -deer species, goat, pig, horse, camel, other). Multiple species can be -selected. If other is selected, enter the species name.
Select the data types that will be recorded for each -quadrat (sign presence only, sign presence by attributable species, -count of each sign, count of each sign by attributable species, age of -sign).
Open the Monitor app and select the Sign-based Fauna Survey +Module and then the Within-plot belt transect protocol.
Select the number of transects to be completed, 1, 2 or +4 (the app will pre-determine which transects to complete based on the +number selected).
Indicate if survey intent is a once-off measure, +repeated measure, or linked to a pre-control activity or post-control +activity (optional).
Indicate the target species (Cat, Fox, Wild dog, Rabbit, +Deer species, Goat, Pig, Horse, Camel). Select ‘Other’ to specify a +species not in the dropdown. Multiple species can be selected/specified. +If there are no target species for this project, select +N/A.
Record the tracking substrate (sand, gravel, mud) or +input a custom value.
Indicate if scats will be counted and left in situ or if -scats will be removed using the check-box.
Enter the number of observers participatingin the -survey, and for each observer, enter the observer name and -observer role (spotter, data entry, data entry only).
For each observer, enter the observer name and +observer role (spotter, data entry).
Enter the weather conditions, including temperature, -rainfall, rainfall duration, cloud cover, wind speed, and moon -phase of the previous night. The weather conditions can be adjusted -after the survey.
Navigate to the S2 transect start point as indicated on the app, -install a peg into the end of a tape measure, and run out the 100 m tape -measure in a straight line directly towards the N2 point. Repeat this -step for the desired numbe of transects (Figure 1).
Navigate to a transect statrt point as indicated on the app (S3 +or N3 for one transect; S2, N2, S4 or N4 for two transects; and S2, N2, +S4, N4, W2, E2, W4 or E4 for four transects) (see Figure 1). Install a +peg into the end of a tape measure, and run out the 100 m tape measure +in a straight line directly towards the corresponding point (e.g. S2 to +N2).
Once all observers are ready and the tape measure is in place, +return to the start point and follow the conduct the survey +steps below.
Figure 1. Plot layouts for the 100 x 100 m core plot 40 x 40 m sub-plot showing available transects.
-+