NE42

NE42 Landscape

Surface Soil

O	0-1 cm	Organic mat; sharp change to:	NE42 Profile
A1	1-8 cm	Brown (7.5YR4/4); fine sandy loam; weak coarse blocky structure; firm consistence dry; contains a common (15%) amount of ferro-manganiferous nodules (5-12 mm size); pH 4.9; abrupt change to:
A2	8-45 cm	Pinkish white (7.5YR7/4) con-spicuously bleached (10YR8/3d) loamy sand; structureless; weak consistence dry; pH 5.6; abrupt and wavy change to:
Subsoil
B21	45-60 cm	Light brownish grey (2.5Y6/2) with yellowish red (5YR5/8) and faint brownish yellow (10YR6/6) mottles; light medium clay; moderate coarse blocky, breaking to moderate medium blocky structure; strong consistence, moderately moist; contains a few (5%) ferromanganiferous nodules (10 mm size); pH 7.6; gradual change to:
B22	60-75 cm	Light brownish grey (2.5Y6/2) with faint brownish yellow (10YR6/6) mottles; light medium clay; weak coarse prismatic, breaking to strong coarse blocky structure; strong consistence, moderately moist; contains a common (10%) amount of manganese stains; pH 8.6; clear change to:
B23	75-95 cm	Light yellowish brown (2.5Y6/4) with olive yellow (2.5Y6/6) diffuse mottles; medium clay; moderate coarse prismatic, breaking to strong coarse blocky structure; strong consistence moderately moist; many slickensides present; pH 8.9; clear change to:
B31k	95-120 cm	Pale brown (10YR6/3); medium heavy clay; strong very coarse prismatic structure; firm consistence moist; contains a few (2-5%) silica and carbonate nodules (2-50 mm size); pH 9.2; clear change to:
B32	120-140 cm	Light olive brown (2.5Y5/4); light medium clay; moderate coarse prismatic, breaking to moderate coarse blocky structure; very firm consistence moderately moist; pH 9.3; gradual change to:
B33	140+ cm	Dark yellowish brown (10YR4/4); sandy clay loam; moderate coarse blocky structure; strong consistence moderately moist; contains a few (5%) manganese stains; pH 9.3;

Key Profile Features:

• Strong texture contrast between surface (A) horizons (<10 % clay) and subsoil (B21) horizon (47 % clay)
• Conspicuously bleached subsurface (A2) horizon.
• Vertic properties (ie. slickensides present) in deeper subsoil.

	The surface horizon is very strongly acid. The subsurface (A2) horizon is moderately acid. The upper subsoil is slightly alkaline and the deeper subsoil becomes very strongly alkaline.		The salinity rating is very low for the upper profile and becomes low at about one metre depth.
	The subsoil is strongly sodic throughout. Strong to complete dispersion occurs.		The clay percentage increases significantly at the A/B horizon interface.

Horizon	Horizon Depth (cm)	pH (water)	pH (CaCl2)	EC 1:5	Organic Carbon G/100g	Exchangeable Cations
						Ca	Mg	K	Na
						meq/100g
A1	1-8	4.9	4.1	0.12		1.1	0.25	0.51	0.14
A2	8-45	5.6	4.4	<0.05		0.28	0.08	0.18	0.06
B21	45-60	7.6	6.1	0.06		3.8	6.5	0.53	1.8
B22	60-75	8.6	7.1	0.11		4.6	9.7	0.61	2.9
B23	75-95	8.9	7.5	0.09		5.3	13	0.6	4.5
B31k	95-120	9.2	8.2	0.3		5.6	14	0.6	4.9
B32	120-140	9.3	8.2	0.23		7.3	12	0.82	3.9
B33	140+	9.3	7.9	0.12		3.8	7.7	0.41	2.8

Horizon	Horizon Depth (cm)	Exchangeable Aluminium mg/kg	Exchangeable Acidity meq/100g	Field Capacity pF 2.5	Wilting Point pF 4.2	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	1-8	55		19.5	5.3	17	54	16	9
A2	8-45	17		15.4	1.7	19	60	16	5
B21	45-60			30.6	18.8	11	32	9	47
B22	60-75			33.8	18.5	6	33	11	50
B23	75-95
B31k	95-120
B32	120-140
B33	140+

Management Considerations:

Whole Profile

• Plant available water capacity (PAWC) is considered to be low (estimated at 80 mm) for the top metre of the soil. This is based on available laboratory data. Effective rooting depth is, however, likely to be significantly lower than 1 metre in this profile due to the strongly sodic subsoil conditions. Therefore, PAWC is likely to be very low.

• In very strongly acid soils, manganese and aluminium solubility can increase to toxic levels. The level of exchangeable aluminium measured in the laboratory is, however, only moderate (55 ug/g) and unlikely to significantly restrict the growth of aluminium sensitive species. A pH/aluminium test performed on a bulked sample (taken across the paddock) would be most appropriate.
• The hardsetting surface soil has a high fine sand and silt content (70 %). Organic matter is therefore very important for maintaining aggregation and preventing slaking. Cultivation in a dry condition can be deleterious to soil structure as the soil will become 'powdery' and subsequent rainfall may result in surface sealing occurring.
• Both surface horizons have a very low nutrient status (based on the sum of the exchangeable basic cations).
• The subsurface (A2) horizon will become 'soupy' when waterlogging occurs on top of the poorly permeable subsoil. This is because of the very high fine sand and silt content and resultant low liquid limit which gives little cohesive strength when saturated.
• The relatively low wilting point value (ie. 5%) indicates that plants will be able to utilise light rains falling on relatively dry soil.

• The subsoil is strongly sodic (and has a low calcium:magnesium ratio) and disperses completely. As a result, subsoil permeability will be very low and aeration will also be restricted.
• The deeper subsoil displays vertic properties (ie. presence of slickensides). This indicates that significant shrinking and swelling occurs in the deeper subsoil.
• Manganese segregations in the subsoil may have a toxic effect on sensitive species.

• Cultivated (1977), disc cultivated (1984)
• Topdressed with 1t/ha lime (1984) and 29 bags super, lime and Mo in 1986.