Gully Density

AUS-TDG-CON-GUL General Moderate confidence

Benchmark Value

No specific value — see range
Direction: Lower is desirable ↓
Form: LowerThreshold

Scoring Curve

This curve shows how a field measurement for this indicator would score across all available benchmark forms in this context. The scoring engine uses 6 benchmarks together — the Point form drives the primary score, while 5 guard(s) constrain the result.

Evidence & Context

The lower critical threshold for active gully density, below which environmental health is significantly compromised in Conservation / Protected Natural Areas within this biome, is effectively any value greater than 0 m/ha.

Metric Definition:

Gully density is quantitatively defined as "the total gully length per area of the whole study area".

Benchmark Definition:

This benchmark defines the lower critical threshold for active gully density, where any value above zero indicates significant environmental degradation in conservation areas of this biome.

Justification:

The presence of any active gully signifies a departure from landscape stability and initiation of soil loss, compromising ecological function and conservation objectives.

Sources (1)

Preview of Ecological Impact Assessment - Whitehaven Coal
Ecological Impact Assessment - Whitehaven Coal Journal

Mokota Conservation Park Management Plan - Department for Environment and Water

View Source

Supporting Sources (14)

Additional references from the underlying research that informed this benchmark.

Preview of A global comparison of soil erosion associated with land use and climate type
A global comparison of soil erosion associated with land use and climate type
Contextual Support Journal

A global comparison of soil erosion associated with land use and climate type

View Source
Preview of Australia's Strategy for the National Reserve System 2009–2030 - DCCEEW
Australia's Strategy for the National Reserve System 2009–2030 - DCCEEW
Contextual Support Journal

Australia's Strategy for the National Reserve System 2009–2030 - DCCEEW

View Source
Preview of Can Coarse Woody Debris Be Used for Carbon Storage in Open Grazed Woodlands?
Can Coarse Woody Debris Be Used for Carbon Storage in Open Grazed Woodlands?
Contextual Support Journal

Can Coarse Woody Debris Be Used for Carbon Storage in Open Grazed Woodlands?

View Source
Preview of Developing good practice guidance for estimating land degradation in the context of the United Nations Sustainable Development Goals | Request PDF - ResearchGate
Developing good practice guidance for estimating land degradation in the context of the United Nations Sustainable Development Goals | Request PDF - ResearchGate
Contextual Support Journal

Developing good practice guidance for estimating land degradation in the context of the United Nations Sustainable Development Goals | Request PDF - ResearchGate

View Source
Preview of Ecological site R075XY059NE - Ecosystem Dynamics Interpretive Tool
Ecological site R075XY059NE - Ecosystem Dynamics Interpretive Tool
Contextual Support Journal

Ecological site R075XY059NE - Ecosystem Dynamics Interpretive Tool

View Source
Preview of Influence of Topographic Factors on the Characteristics of Gully Systems in Mountainous Areas of Ningnan Dry-Hot Valley, SW China - PubMed Central
Influence of Topographic Factors on the Characteristics of Gully Systems in Mountainous Areas of Ningnan Dry-Hot Valley, SW China - PubMed Central
Contextual Support Journal

Influence of Topographic Factors on the Characteristics of Gully Systems in Mountainous Areas of Ningnan Dry-Hot Valley, SW China - PubMed Central

View Source
Preview of National Reserve System protected area requirements - DCCEEW
National Reserve System protected area requirements - DCCEEW
Regulatory Framework Government

National Reserve System protected area requirements - DCCEEW

View Source
Preview of Nitrogen use efficiency and nitrogen balance in Australian farmlands - Agronomy Australia Proceedings, accessed May 11, 2025
Nitrogen use efficiency and nitrogen balance in Australian farmlands - Agronomy Australia Proceedings, accessed May 11, 2025
Contextual Support GreyLiterature

Letnic, M. (2019). What are native grasslands, and why do they matter? UNSW Newsroom.

View Source
Preview of OFFICIAL - DCCEEW
OFFICIAL - DCCEEW
Contextual Support Journal

OFFICIAL - DCCEEW

View Source
Preview of parks - IUCN Portals
parks - IUCN Portals
Contextual Support Journal

parks - IUCN Portals

View Source
Preview of Soil erosion impacts on crop yields in North America. Adv Agron - ResearchGate
Soil erosion impacts on crop yields in North America. Adv Agron - ResearchGate
Contextual Support Journal

Soil physical properties of the studied gully sidewall (means ± standard error). - ResearchGate

View Source
Preview of Sydney Drinking Water Catchment Audit 2019-22 - WaterNSW
Sydney Drinking Water Catchment Audit 2019-22 - WaterNSW
Contextual Support Journal

Sydney Drinking Water Catchment Audit 2019-22 - WaterNSW

View Source
Preview of The International Journal of Protected Areas and Conservation
The International Journal of Protected Areas and Conservation
Contextual Support Journal

The International Journal of Protected Areas and Conservation

View Source
Preview of Woodlands - DCCEEW, accessed August 5, 2025,
Woodlands - DCCEEW, accessed August 5, 2025,
Contextual Support

Woodlands - DCCEEW, accessed May 19, 2025

View Source

Context

  • Region Australia
  • Biome Temperate Dry Woodlands & Native Grasslands
  • Land Use Conservation / Protected Natural Areas
  • Assessment Conservation Target
  • Evidence Type DegradationThreshold

Lifecycle

  • Status Active
  • Version 1
  • Effective From 24 Mar 2026

Notes

Any active gully density > 0 m/ha is considered critical, indicating compromised ecological function and active degradation. ConsistencyResolver applied 2026-03-24 20:09 UTC: LowerThreshold 0 → (check: MinEqualsMax, rationale: The Notes indicate that any gully density > 0 is detrimental, so the threshold is an upper limit, not a lower limit. Since a MaximumOnly threshold at 0 already exists (ID=1931), the MinimumOnly threshold at 0 is redundant and causes a zero-width range. Setting LowerThreshold to null removes this conflict and resolves the issue.) ConsistencyResolver applied 2026-03-24 20:20 UTC: BenchmarkValue 0 → (check: MinEqualsMax, rationale: The Notes indicate that any gully density > 0 is detrimental, so the threshold is an upper limit, not a lower limit. Removing the BenchmarkValue from the MinimumOnly benchmark removes the zero-width range conflict and aligns with ecological interpretation.) ConsistencyResolver applied 2026-03-24 20:20 UTC: UpperThreshold → (check: MinEqualsMax, rationale: No UpperThreshold should be set on the MinimumOnly benchmark to avoid duplication and maintain the correct threshold direction.) ConsistencyResolver applied 2026-03-24 20:20 UTC: LowerThreshold → (check: MinEqualsMax, rationale: No LowerThreshold is needed on the MinimumOnly benchmark because the ecological threshold is an upper limit at 0, already represented by the MaximumOnly benchmark.) ConsistencyResolver applied 2026-03-24 20:20 UTC: BenchmarkValue → (check: MinEqualsMax, rationale: The MinimumOnly benchmark should not have a threshold value since the upper limit at 0 is already defined by the MaximumOnly benchmark (ID=1931). Clearing any BenchmarkValue or threshold fields from this benchmark removes the zero-width range conflict.) ConsistencyResolver applied 2026-03-24 20:21 UTC: BenchmarkValue → (check: MinEqualsMax, rationale: The MinimumOnly benchmark should not have a threshold value since the upper limit at 0 is already defined by the MaximumOnly benchmark (ID=1931). Clearing any BenchmarkValue or threshold fields from this benchmark removes the zero-width range conflict.) ConsistencyResolver applied 2026-03-24 20:21 UTC: UpperThreshold → (check: MinEqualsMax, rationale: No UpperThreshold should be set on the MinimumOnly benchmark to avoid duplication and maintain the correct threshold direction.) ConsistencyResolver applied 2026-03-24 20:21 UTC: LowerThreshold → (check: MinEqualsMax, rationale: No LowerThreshold should be set on the MinimumOnly benchmark to avoid duplication and maintain the correct threshold direction.) ConsistencyResolver applied 2026-03-24 20:21 UTC: LowerThreshold → (check: MinEqualsMax, rationale: No LowerThreshold should be set on the MinimumOnly benchmark because the ecological threshold is an upper limit at 0, already represented by the MaximumOnly benchmark (ID=1931).) ConsistencyResolver applied 2026-03-24 20:21 UTC: UpperThreshold → (check: MinEqualsMax, rationale: No UpperThreshold should be set on the MinimumOnly benchmark to avoid duplication and maintain the correct threshold direction.) ConsistencyResolver applied 2026-03-24 20:22 UTC: BenchmarkValue → (check: MinEqualsMax, rationale: The MinimumOnly benchmark should not have a threshold value since the upper limit at 0 is already defined by the MaximumOnly benchmark (ID=1931). Clearing any BenchmarkValue or threshold fields from this benchmark removes the zero-width range conflict.)