SW62

SW62 Landscape

Soil Profile Morphology:

Surface Soil

A1	0-40 cm	Black (10YR2/1 moist, 10YR4/1 dry); loamy fine sand; massive firm consistence; pH 4.3; gradual and wavy change to:	SW62 Profile
A2g	40 cm+	Very dark greyish brown (10YR3/2 moist and 10YR5/2 dry), becoming mottled with depth (90 cm+); loamy fine sand; massive firm consistence; pH 4.7.

	pH	Salinity Rating	Sodicity	Dispersion
Surface (A1 horizon)	Extremely Acid	Low	Non-Sodic	-
Subsurface (A2) horizon)	Very Strongly Acid	Low	Non-Sodic	-

Horizon	Horizon Depth (cm)	pH (water)	pH (CaCl2)	EC 1:5	NaCl %	Exchangeable Cations
						Ca	Mg	K	Na
						meq/100g
A1	0-40	4.3	3.4	0.13		0.35	0.53	0.09	0.62
A2g	40+	4.7	4	<0.05		<0.05	0.09	<0.05	0.1

Horizon	Horizon Depth (cm)	Ex Al mg/kg	Ex Ac meq/100g	Field pF2.5	Wilting Point pF4.2	Coarse Sand (0.2- 2.0 mm)	Fine Sand (0.02- 0.2 mm)	Silt (0.002- 0.02 mm)	Clay (<0.002 mm)
A1	0-40	230	18			19	49	23	5
A2g	40+	110	5.9			28	47	19	6

Management Considerations:

Whole Profile

• The soil profile is likely to be saturated for a number of months during most years.

• Exchangeable aluminium levels are high in the extremely acid surface soil. This will restrict the growth of aluminium sensitive species. High levels of aluminium will also tend to “fix” phosphorus and make it less available to plants (and therefore reduce the effectiveness of applied P fertilisers). Raising the pH level of the soil by liming will help reduce the level of exchangeable aluminium. A lime test (sampled across the whole paddock) may be appropriate to determine the amount of lime needed to raise pH. Other factors need to be considered, however, before lime is recommended (e.g. species growth, method of application, trial response, likely cost benefit).
• Manganese toxicity can occur in strongly acid soils, especially when waterlogging occurs. Raising the pH by lime application will assist in reducing any manganese toxicity.