Soil Phosphorus

AUS-TMS-AGR-SOP General Low confidence

Benchmark Value

40 mg/kg
Thresholds: Lower: —, Upper: 40
Direction: Higher is desirable ↑
Form: UpperThreshold

Scoring Curve

This curve shows how a field measurement for this indicator would score across all available benchmark forms in this context.

Evidence & Context

For sandy soils with Extremely Low to Very Low PBI (e.g., PBI <35-70): Colwell-P levels moderately exceeding the agronomic optimum, potentially > 30-40 mg/kg, should be considered approaching or exceeding a detrimental threshold

Metric Definition:

soil phosphorus refers primarily to plant-available phosphorus fractions, with a focus on measurements obtained via the Colwell-P test (expressed in mg/kg)

Benchmark Definition:

This benchmark represents the upper detrimental threshold of plant-available soil phosphorus (Colwell-P) above which environmental risks such as leaching and runoff increase significantly in sandy soils with low phosphorus buffering capacity under agricultural crop production in tropical monsoonal savannas.

Justification:

Due to the high risk of P leaching and runoff. For these soils, the capacity to retain surplus P is minimal.

Sources (1)

Preview of Soil phosphorus–crop response calibration ... - CSIRO Publishing, accessed May 11, 2025,
Soil phosphorus–crop response calibration ... - CSIRO Publishing, accessed May 11, 2025, Journal

Soil phosphorus–crop response calibration relationships and criteria for winter cereal crops grown in Australia - CSIRO Publishing

View Source

Supporting Sources (3)

Additional references from the underlying research that informed this benchmark.

Preview of Based on levels indicating severe P deficiency for plant growth and likely impairment of soil ecological functions (e.g., microbial activity, nutrient cycling), drawing from S18, S43, S44, S50 (interpreted for cropping context).
Based on levels indicating severe P deficiency for plant growth and likely impairment of soil ecological functions (e.g., microbial activity, nutrient cycling), drawing from S18, S43, S44, S50 (interpreted for cropping context).
Direct Evidence

Based on levels indicating severe P deficiency for plant growth and likely impairment of soil ecological functions (e.g., microbial activity, nutrient cycling), drawing from S18, S43, S44, S50 (interpreted for cropping context).

Preview of Based on levels where P loss to the environment (leaching/runoff) becomes a significant risk, or where potential for P toxicity or nutrient imbalances may arise. Threshold is highly dependent on soil PBI, texture, and hydrology.
Based on levels where P loss to the environment (leaching/runoff) becomes a significant risk, or where potential for P toxicity or nutrient imbalances may arise. Threshold is highly dependent on soil PBI, texture, and hydrology.
Direct Evidence

Based on levels where P loss to the environment (leaching/runoff) becomes a significant risk, or where potential for P toxicity or nutrient imbalances may arise. Threshold is highly dependent on soil PBI, texture, and hydrology.

Preview of Derived synthesis from 1, S26, S41, S55, S56, S68, with ecological interpretation and adjustment for regenerative principles.
Derived synthesis from 1, S26, S41, S55, S56, S68, with ecological interpretation and adjustment for regenerative principles.
Direct Evidence

Derived synthesis from 1, S26, S41, S55, S56, S68, with ecological interpretation and adjustment for regenerative principles.

Context

  • Region Australia
  • Biome Tropical Monsoonal Savannas
  • Land Use Agricultural Crop Production
  • Assessment Not Stated
  • Evidence Type DegradationThreshold

Lifecycle

  • Status Active
  • Version 1
  • Effective From 1 Jun 2026

Notes

Threshold is highly dependent on soil PBI, texture, and hydrology. Upper Detrimental Threshold: 40 mg/kg. AssessmentContext defaulted to 'Not Stated' because the source document did not state one.