{{ summaryTitle }}
{{ summaryValue }}
{{ summaryLine }}
{{ badge.label }} {{ badge.value }}
Area · {{ formatArea(values ? values.area_m2 : 0) }} Depth · {{ formatDepth(values ? values.depth_m : 0) }}
Bed measurement, soil-test targets, and amendment planning inputs
to
to%

Product strength defaults are neutral; gypsum, logistics, package sizes, and prices stay off until you enter them.

%
%
Enable only for a diagnosed soil need; it does not replace pH correction.
{{ include_gypsum ? 'Enabled' : 'Disabled' }}
$
$
$
$
{{ tableExportStatus }}
Field sheet listing planned amendments, quantity, application rate, packages, and cost.
MaterialQuantityRatePackagesCostCopy
{{ row.material }}{{ row.quantity }}{{ row.rate }}{{ row.packages }}{{ row.cost }}

Canonical quantities use SI units. Package counts round upward only when an optional supplier package size is entered.

Staging plan with phase, field action, checkpoint, and row copy.
PhaseField actionCheckpointCopy
{{ row.phase }}{{ row.action }}{{ row.checkpoint }}
{{ chartExportStatus }}

Mass supports transport planning; compost volume remains the field-spreading quantity. Supplier bulk density controls its mass.

Introduction:

A soil amendment plan begins with a mismatch: the soil test describes the bed as it is, while the crop or planting plan defines where it needs to go. The work may involve adding organic matter, raising pH with lime, lowering pH with elemental sulfur, or leaving a value alone. These materials are not interchangeable, and applying more than the soil needs can be harder to correct than applying too little.

Soil pH describes acidity or alkalinity on a logarithmic scale. It affects nutrient availability and root conditions, but it does not say how much material will move a particular soil to a target pH. Sandy soil usually changes more readily than clay-rich or organic soil because the latter can resist pH change. A laboratory lime-requirement or buffer test therefore gives a stronger basis for liming than pH alone.

Organic matter
The carbon-rich fraction reported by a soil test. Compost can improve structure and water handling, but its density, salts, maturity, and nutrient content vary by product.
CCE
Calcium carbonate equivalent, a product-strength measure for lime. A lower CCE means more product is needed to supply the same neutralizing capacity.
Assay
The percentage of active elemental sulfur in a product. Diluted products need a larger total mass than pure sulfur for the same active amount.

Compost planning is a volume problem before it becomes a weight problem. Bed area and incorporation depth determine the soil volume being treated, while the organic-matter gap sets the planning amount. Bulk density then converts compost volume into transport mass. Bags, wheelbarrow loads, and prices are purchasing details added after the amendment quantity is known.

A calculated quantity is a staging estimate, not an application prescription. Soil-test methods, regional recommendations, crop sensitivity, product labels, and existing nutrient or salt levels can all change the correct treatment. Large sulfur applications should be split and followed by retesting; gypsum should be included only for a diagnosed need and does not correct pH.

How to Use This Tool:

Start with a recent, representative soil test and measure only the bed area and depth that will actually be amended.

  1. Choose a Soil goal profile or set custom pH and organic-matter targets for the crop. Treat a profile as a starting point and replace it when local guidance gives a better target.
  2. Enter Bed area, Incorporation depth, and Soil texture. Use the prepared depth through which the material will be mixed, not the full depth of the bed.
  3. Enter the current and target pH and organic-matter percentages. For a pH increase, choose Entered lab lime rate whenever the report provides a requirement per 0.1 pH unit.
  4. Set compost density, lime CCE, and sulfur assay from the supplier or product label. Enable gypsum only when a soil diagnosis supports it.
  5. Add package sizes, prices, or wheelbarrow capacity only when purchasing and staging estimates are needed. Review the Field Sheet for quantities and the Staging Plan for application and retest cues.

Interpreting Results:

Read compost by volume for spreading and by mass for transport. Package counts are rounded up to whole bags, so the purchased amount can exceed the calculated requirement. A zero package count means no usable package size was entered, not that the amendment quantity is necessarily zero.

  • Texture planning estimate is a transparent screening method. Confirm lime or sulfur with a laboratory recommendation before applying a consequential amount.
  • A zero lime or sulfur result means the target does not call for movement in that direction. Lime is calculated only for a higher target pH; sulfur only for a lower target pH.
  • If the sulfur rate reaches 4 lb per 100 ft², the plan calls for two passes. Retest after the material has reacted instead of applying the whole change again from the original result.

Technical Details:

All measurements are converted to square metres, metres, cubic metres, and kilograms for the result. The pH branch is chosen from the sign of the target change, while the organic-matter branch ignores negative gaps. Intermediate values retain full precision; displayed values may be rounded.

Formula Core:

The organic-matter gap cannot fall below zero, so a target at or below the current test produces no compost quantity.

ΔOM=max(0,OMtarget-OMcurrent)

The compost heuristic uses bed area in square feet, incorporation depth in inches, and the organic-matter gap in percentage points. The result is converted from cubic yards to cubic metres, then multiplied by the entered bulk density for transport mass.

Vcompost=Aft21000×Din6×ΔOM×0.75

For a pH increase, the preferred lab-rate path scales the entered requirement by area, tenths of a pH unit, and lime strength. The texture path replaces the lab rate with a planning factor per 100 ft² per pH unit.

Mlime=Aft21000×ΔpH0.1×Rlab×100CCE

Rule Core:

Texture factors are planning constants, not universal agronomic rates. Lime and sulfur strength corrections divide by the entered percentage; gypsum has no strength adjustment.

Soil texture planning factors per one hundred square feet and one pH unit
TextureLime factorSulfur factorOptional gypsum
Sandy loam3.5 lb0.9 lb2.0 lb
Loam4.5 lb1.2 lb2.8 lb
Clay loam6.0 lb1.5 lb3.6 lb
Heavy clay7.5 lb1.8 lb4.5 lb

Whole-package and wheelbarrow counts use a ceiling, so any positive remainder requires another unit. Cost equals the rounded package count multiplied by its entered price. Bed area and incorporation depth must be positive; pH is accepted from 2.5 to 10, organic matter from 0% to 30%, CCE above 0% through 200%, and sulfur assay above 0% through 100%.

Accuracy Notes:

The compost, texture, sulfur, and gypsum quantities are planning heuristics. Real response depends on laboratory method, buffering capacity, clay and organic matter, climate, incorporation, moisture, product fineness, and time.

  • Use the laboratory's lime requirement when available and follow local crop guidance and the product label.
  • Do not use the gypsum option as a general clay remedy or pH treatment; include it only for a diagnosed soil condition.
  • Retest at a comparable time and sampling depth after the amendment has had time to react.

Worked Examples:

Lab lime rate with package rounding

A 300 ft² clay-loam bed moving from pH 5.4 to 6.7 uses an entered rate of 8 lb per 1,000 ft² for each 0.1 pH increase. With 90% CCE, the model produces about 34.67 lb, or 15.72 kg, of lime. Ten-kilogram bags round up to two packages, so an entered price of $18 per bag produces a $36 purchase estimate.

References: