Skip to content
Menu
LandWISE – Promoting sustainable land management
  • Welcome
    • About
    • LandWISE Committee
    • Contact
  • Projects
    • Carbon Positive
      • Carbon Positive Reports
    • Nitrachek: Farmer Friendly Nitrate Testing
    • SLAKES: a cost-effective measure of soil structural stability
    • Soil Repair after Cyclone Gabrielle
    • Vegetable Production Nitrogen Management
    • Best Management of Nitrates in Process Cropping
    • Future Proofing Vegetable Production
    • Herbicide Resistance Management
  • Events
    • Cyclone Gabrielle Research Symposium
      • Historical North Island Flood Events
      • An extraordinary storm: the severity of Cyclone Gabrielle’s weather in Hawke’s Bay
      • The Science Response in the Year of Storms; A Gisborne/Tairawhiti perspective
      • Insights into causes of landslides triggered by Cyclone Gabrielle
      • The effects of Cyclone Gabrielle on fruit tree health in Hawke’s Bay
      • Impact of Cyclone Gabrielle on stonefruit orchards in Hawke’s Bay: a case study
      • Charting the Course following Cyclone Gabrielle
      • Baseline sediment sampling in Tairawhiti and Hawke’s Bay
      • Impacts on cropping businesses
      • Understanding the flooding caused by Cyclone Gabrielle
      • Building Flood Damage from Ex-Tropical Cyclone Gabrielle
      • Food safety and critical incidents: A unified approach for safer produce
      • Silt nutritional status and contamination concerns
      • Lessons from the horticultural sector response to Cyclone Gabrielle
      • Ecological impacts of Cyclone Gabrielle
      • Cyclone Gabrielle and Poplar Windthrow in Northland
      • Seed Size and Establishment Method Determine Crop Recovery Following Cyclone-Induced Silt Deposition
      • Returning to (some) baseline sampling sites to assess cropping soil recovery
      • Recovery of annual cropping ground – Grower learnings
      • Recovery of Annual Cropping over 2 Years
      • Technical and extension learnings from Cyclone Gabrielle
    • Getting to Carbon Positive!
      • Getting to Carbon Positive – Presenters
    • Rebuilding Our Soils
      • Rebuilding Our Soils – Presenters
    • Events Archive
  • Tools
    • Nitrachek Calculator
    • Carbon Calculator
    • Nutrient Budget
    • Irrigation Evaluation – IRRIG8
      • IRRIG8: Centre Pivot
        • IRRIG8-online: Centre Pivot User Guide
      • IRRIG8: Linear Move
      • IRRIG8: Travelling Irrigator
        • IRRIG8-online: Travelling Irrigation User Guide
      • IRRIG8: Multiple sprayline calculator
      • IRRIG8: Solid set irrigation
      • IRRIG8: Pressure and energy
        • Pressure and Energy Calculator: User Guide
    • ANOVA Tool for statistical significance
    • Fertspread Spreader Calibration
    • Fertspread Placement Calibration
    • Soil Infiltration Calculator
      • Disc Permeameter User Guide
      • Disc Permeameter Calculator: Frequently Asked Questions
  • Blog
  • Sign Up
  • Login
  • Members Only
    • Online Learning
  • Account
  • Site Search
LandWISE – Promoting sustainable land management

Disc Permeameter User Guide

Measure unsaturated hydraulic conductivity, characterise pore-size structure, and compare soil health across treatments and depths.

1. What This Calculator Does

The Disc Permeameter Infiltration Calculator processes field data from disc permeameter (tension infiltrometer) measurements to calculate unsaturated hydraulic conductivity K(h). It helps you answer: how quickly does water move through different pore sizes in your soil, and how does soil structure vary between treatments, depths, and sites?

The calculator operates in two modes:

ModeDescription
Quick CalculatorEnter reservoir readings from a single tension measurement. The calculator detects steady-state infiltration, applies the Wooding equation, and computes K(h). Includes an option to estimate the sorptive number a* from multi-tension data.
Batch AnalysisUpload a CSV file containing field data from multiple sites, tensions, and depths. The tool computes K(h) for every measurement, generates summary tables grouped by treatment and depth, produces pore-class charts, and exports downloadable reports.

All calculations happen in your browser. No data is sent to a server.

2. Key Concepts

The Wooding Equation

The calculator uses the Wooding (1968) steady-state equation to convert observed infiltration rates into hydraulic conductivity:

K(h) = q_ss / (1 + 4 / (π · a* · r))

where q_ss is the steady-state flux (cm/s), a* is the sorptive number (cm⁻¹) that describes how strongly the soil draws water by capillarity, and r is the disc radius (cm).

Sorptive Number (a*)

a* controls how much of the infiltration is driven by capillarity versus gravity. It can be obtained in two ways:

• Known value: Enter a published or previously determined a* directly. Use 0.05 cm⁻¹ as a reasonable default for most agricultural soils.

• Estimate from data: If you have steady-state rates at multiple tensions, the calculator fits a regression of ln(q) versus h. The slope of that line is a*. The R² value indicates fit quality.

Pore-Size Bands

By running the disc permeameter at multiple tensions (e.g. −15, −6, −3 cm), you introduce progressively larger pores. Subtracting consecutive K(h) values isolates how much water flows through each pore-size band:

Tension (cm)Approx. max pore diameterWhat it represents
−15~0.2 mmFlow through the finest measurable pores only
−6~0.5 mmAdds medium structural pores
−3~1.0 mmAdds coarse structural pores (inter-aggregate cracks, fine root paths)

Note: even the coarsest band measured (−3 cm, pores up to ~1 mm) is finer than visible earthworm burrows or large root channels, which only flow under ponded conditions.

Steady-State Detection

The calculator automatically identifies when infiltration has reached steady-state by examining the last N readings (default 6). It checks both the coefficient of variation (CV%) and the slope of the readings over time. You can adjust these thresholds under Advanced Settings in the header.

Units

All results are displayed in mm/hr as the primary unit, with cm/s shown as a secondary value. The CSV input uses cm/min for reservoir drop rate (as read in the field), and the calculator handles all conversions internally.

Statistical Reporting

The calculator reports mean values ± standard error for all summary statistics. This approach is more appropriate than median values for the typical small sample sizes (3–5 replicates) used in infiltration studies, as means utilize all data points and provide better statistical power. Standard errors quantify the precision of mean estimates and enable proper statistical comparisons between treatments.

Quality Control System

The calculator automatically detects physically impossible data where K(h) decreases with less negative heads (e.g., K(-15) > K(-6)), which typically indicates insufficient equilibration time. When violations are detected, users can choose to:

• Remove problematic measurements only (recommended): Excludes only the problematic tensions while retaining valid measurements for partial pore-class analysis

• Exclude entire affected sites: Removes whole sites with any violations

• Keep all data anyway: Proceeds with clear warnings about data quality issues

Partial data analysis allows calculation of pore classes from remaining valid measurements (e.g., if K(-15) is problematic but K(-6) < K(-3) is valid, the -6 to -3 pore class can still be calculated).

All results are displayed in mm/hr as the primary unit, with cm/s shown as a secondary value. The CSV input uses cm/min for reservoir drop rate (as read in the field), and the calculator handles all conversions internally.

3. Configurable Parameters

Four parameters appear in the green header banner and can be edited at any time. Changes take effect immediately for subsequent calculations.

ParameterDefaultNotes
Disc diameter (cm)20Outer diameter of your disc permeameter base. Common sizes: 20 cm (standard), 25 cm (large).
Reservoir diameter (cm)5.4Inner diameter of the water reservoir tube.
Soil depths (cm)0, 10Comma-separated list of measurement depths. Typically surface (0) and a subsurface depth.
Tensions (cm)−15, −6, −3Comma-separated list of applied tensions (most negative first). These drive the dynamic inputs throughout the calculator.

Advanced Settings

Click “Advanced settings” in the header to reveal tail-detection parameters:

ParameterDefaultWhat it controls
Tail points (N)6Number of final readings used to assess steady-state.
Tail CV threshold (%)20Maximum coefficient of variation for the tail to be considered stable.
Tail slope threshold0.00001Maximum absolute slope (cm s⁻¹ min⁻¹) allowed in the tail. A near-zero slope indicates steady flow.

 

4. Quick Calculator

Use this tab for processing individual measurements interactively.

Step 1 – Sorptive Number (a*)

Choose one of two modes using the radio cards:

• Use a known value: Enter a* directly. Typical range is 0.01–0.5 cm⁻¹. If unsure, use 0.05.

• Estimate from my data: Enter your own steady-state infiltration rate determined at each configured tension. Click “Estimate a” to run a ln(q) vs h regression. If the fit is acceptable (R² close to 1), click ”Use this a” to transfer it to Step 2.

Step 2 – Enter Reservoir Readings

Enter your time-series of reservoir readings for a single tension run:

  1. Set the tension h (cm) for this run.
  2. Enter time (minutes) and reservoir level (cm) readings. New rows are added automatically when you fill the last row.
  3. Click “Calculate K(h)”.

The calculator converts reservoir drop to disc-surface flux using the conversion factor (reservoir area / disc area), identifies the steady-state tail, and applies the Wooding equation.

Results

A results panel displays:

  • K(h) in mm/hr (highlighted) and cm/s
  • Steady-state rate (the detected constant infiltration rate)
  • Wooding factor = 1 + 4/(π·a·r), showing the capillarity correction
  • Quality indicators: tail CV%, slope, and status message (either ✓ Steady-state acceptance checks passed* or warning messages if the CV or slope threshold is exceeded)

More details

Expand “Calculation details” for a step-by-step breakdown of the computation. You can also download the entered data as a CSV.

5. Batch Analysis

Use this tab when you have a complete field dataset to analyse.

CSV Format

Your CSV must contain these columns (header names must match exactly):

ColumnDescriptionExample
DateDate of measurement2025-03-15
TreatmentTreatment or land-use nameConventional
PlotPlot or site number1
SubsampleSubsample or replicate ID1
Soil depth (cm)Measurement depth0
Head (cm)Applied tension−6
Constant rate (cm/min)Steady-state reservoir drop rate0.0123

Click “Download example CSV template” to get a pre-formatted file for your configured depths and tensions.

Building the Summary

  1. Upload your CSV file. A preview shows the first 3 rows and column headers.
  2. Click “Build Summary”. The calculator parses every row, groups by treatment/plot/depth, estimates a* from the multi-tension data for each group, and computes K(h) at every tension using the Wooding equation.

Depth and tension matching: CSV values are snapped to your configured depths and tensions with ±0.6 cm tolerance. Values outside this range are dropped and noted in the quality report.

Summary Tables

One table is generated per configured depth. Rows are grouped by treatment and plot, showing mean K(h) ± standard error at each tension (in mm/hr), the mean a* ± standard error, and the number of replicates (n). This provides a direct comparison of hydraulic performance across treatments.

Data Quality Report

A summary of any data issues encountered during processing:

  • Rows dropped due to unrecognised depths or tensions
  • Rows with missing or non-numeric rates
  • Groups with insufficient tensions for a* estimation

Use this to identify data entry errors or field measurement problems before relying on the results.

Downloads

Four export options become available after building the summary:

ExportContentsUse for
Summary CSVMean K(h) ± SE by treatment, plot, and depthQuick overview, sharing with collaborators
Full Data CSVEvery measurement row with all computed K(h) valuesAudit trail, custom analysis in R or Excel
Porosity Proxies CSVPore-class conductance (incremental K between tensions) by treatmentPore-structure comparison across treatments
Pore-Class Charts (PDF)Box plots, absolute and percentage stacked bars, and executive summary tablesReports, presentations, printing

6. Understanding the Charts

Box Plots

One box plot is generated for each tension at each depth. Each box shows the distribution of K(h) values across plots for that treatment. The box spans the interquartile range (Q1 to Q3), the line inside is the median, and the whiskers extend to the minimum and maximum. Use these to see variability within treatments and spot outliers.

Note: Box plots correctly show medians as the center line, which is appropriate for displaying
distributions of individual measurements, even though summary tables use means for statistical analysis.

Absolute Stacked Bars (mm/hr)

Each bar shows the total near-saturated conductivity for a treatment, broken into segments for each pore-size band. The height of each segment represents the incremental flow through that pore-size band:

  • Bottom segment (finest pores): K at the most negative tension (e.g. K(−15))
  • Middle segments: Incremental K between consecutive tensions
  • Top segment (coarsest pores): Incremental K at the least negative tension

How to read: Taller bars mean more total infiltration. If most of the bar is in the bottom segment, the soil lacks structural porosity. Large contributions in the upper segments indicate well-developed inter-aggregate pore networks and fine root paths.

Percentage Stacked Bars (% of total flow)

Every bar is scaled to 100%, showing what proportion of total flow goes through each pore-size band. This makes it easy to compare pore structure between treatments regardless of differences in total infiltration rate. Percentage labels appear inside each segment where space permits.

Executive Summary (Traffic-Light Tables)

One table per pore-size band at each depth. Each cell shows conductance in mm/hr, colour-coded against the dataset quartiles:

ColourMeaningThreshold
GreenHigher flow≥ Q3 value for that band
AmberModerate flowBetween Q1 and Q3
RedLower flow — may indicate compaction< Q1 value for that band
GreyNo dataMissing measurement

Note: groups will not always split evenly into quartiles. When multiple sites share similar values they receive the same colour, so ties — common in small datasets — can shift the apparent distribution between colour bands.

7. Quick Start Guide

For a single measurement (Quick Calculator):

  1. Set your equipment dimensions in the header banner (disc and reservoir diameters).
  2. Choose your a* method in Step 1. If you have multi-tension rates, use “Estimate from my data”. Otherwise enter a known value (0.05 if unsure).
  3. Enter your time-series readings in Step 2. Set the tension, then enter time and reservoir level pairs.
  4. Click “Calculate K(h)” and review the results panel.

For a full field dataset (Batch Analysis):

  1. Configure depths and tensions in the header to match your field protocol.
  2. Download the CSV template and enter your data (or format your existing spreadsheet to match).
  3. Upload the CSV on the Batch Analysis tab. Check the preview.
  4. Click “Build Summary” and review the tables and quality report.
  5. Download your exports — summary CSV for quick results, pore-class PDF for presentations.

8. Tips for Best Results

• Run tensions in order from most negative to least negative (−15 → −6 → −3 cm) to avoid wetting hysteresis effects.

• Take frequent early readings (every minute for the first 10 minutes) and space them out as the rate stabilises.

• Ensure good contact between the disc and the soil surface. Use a thin (2–3 mm) layer of fine sand on the prepared surface.

• A minimum of three tensions is needed to estimate a*. Two tensions will give a regression but with no degrees of freedom to assess fit quality.

• If the tail CV exceeds the configured threshold, the run likely did not reach steady-state. Consider extending the measurement or discarding the reading.

• For batch analysis, consistent column naming matters. Use the template CSV to avoid formatting issues.

• If your field data uses different depths or tensions than the defaults, update the header fields before uploading — the calculator will snap CSV values to whatever you configure.

• The calculator is entirely client-side. Your data stays in your browser and is never uploaded to a server. Refresh the page to clear all data.

9. Limitations

• Disc permeameters measure near-saturated conductivity only. They do not characterise micropores (< 0.03 mm) or true saturated conductivity.

• The practical lower tension limit is approximately −15 to −20 cm, constrained by the membrane air-entry value.

• The Wooding equation assumes homogeneous, isotropic soil beneath the disc. Layered or cracked soils may violate this assumption.

• Even at −3 cm tension, pores larger than ~1 mm are excluded. Visible earthworm burrows, root channels, and structural cracks only conduct water under ponded (positive head) conditions.

• Steady-state detection is automated but not infallible. Always review the quality indicators and consider the field context. Make quick checks in the field – if the infiltration rate at a lower tension is less than at a higher tension, it is very likely the higher tension was not run long enough to truly stabilise. You should re-run your measurements to avoid uncalculatable results later.

• The batch analysis uses mean values when summarising across replicates. Standard errors provide appropriate measures of uncertainty around the mean estimates.

10. Quality Control:

The calculator automatically detects physically impossible data (e.g., K(-15) > K(-6)) and offers options to exclude problematic measurements while retaining valid data for partial analysis.

DISCLAIMER

This tool was developed by LandWISE Inc. to support soil health research and monitoring. It is not a commercial product and must not be relied on for critical decision-making without independent verification. We make no warranties and take no responsibility for any errors in the calculator or its outputs. Use it at your own risk. It is made freely available solely on this basis.

Disc Permeameter Infiltration Calculator v1.0.2 — landwise.org.nz — February 2026

  • Cyclone Gabrielle Research Symposium
  • Biodiversity Strips Update
  • Carbon Positive: Butternuts
  • Carbon Positive: Butternut Planting to Side Dressing
  • Nitrate Levels on the MicroFarm
  • Cyclone Gabrielle Research Symposium
  • Introducing Carys Luke, our Summer Intern
  • Soil Infiltration Calculator
  • MicroFarm Biodiversity Update
  • Irrigation System Testing
  • Carbon Positive: Butternut Planting
  • NZARM Conference 2025

RECENT POSTS

  • Cyclone Gabrielle Research Symposium
  • Biodiversity Strips Update
  • Carbon Positive: Butternuts
  • Carbon Positive: Butternut Planting to Side Dressing
  • Nitrate Levels on the MicroFarm

CATEGORIES

  • Agritech
  • Asparagus
  • Conference
  • Courses
  • Cover crops
  • Cultivation
  • Events
  • Fresh Vegetables
  • Irrigation
  • Membership
  • Nitrate
  • Nutrition
  • People
  • Permanent crops
  • Pests
  • Process Crops
  • Projects
  • Protected cropping
  • regenerative agriculture
  • Regulations
  • Research
  • soil health
  • Sustainable technology
  • Uncategorized
  • Water resources
  • Weeds
©2023 LandWISE – Promoting sustainable land management

Disclaimer: Any information on the LandWISE website or linked LandWISE resources is of a general nature only. We endeavour to provide accurate and adequate information relating to the subject matters contained in it. It has been prepared and made available to all persons and entities strictly on the basis that LandWISE, its researchers and authors are fully excluded from any liability for damages arising out of any reliance in part or in full upon any of the information for any purpose. No endorsement of named products is intended nor is any criticism of other alternative, but unnamed product.