Crop Report – August 11, 2021

Figure 3. Soil failure pattern created by a winged tine. Note the vertical fissures. (From Godwin and Spoor, 2015, after Spoor, 2006)

Successful Subsoiling?

Figure 1. Subsoiler setup - does it matter?
Figure 1. Subsoiler setup – does it matter?

 

 

 

 

 

 

 

In many fields, the month of August means the end of cereal harvest and the beginning of a window of opportunity. In many ways, this is the best time of the season for soil improvements beyond what small grains already provide. Applying manure, seeding cover crops, or maybe trying to bury the mistakes of the past for a fresh start.

Seeking a fresh start, some growers look to subsoiling to “fix” compaction. But does it work? Is successful subsoiling possible?

Subsoiling should be a “last resort” option restore function in severely damaged soil. It should not be a necessary and regular part of a cropping system. If it is, the source of the damage should be identified, and the cropping system modified to remove or mitigate it as much as possible.

Types of compaction

The type, depth, and severity of compaction also determine what kind of mechanical remediation should be targeted with subsoiling. Broadly, there are three categories of compaction:

  1. Surface layer compaction – contained within the topsoil, caused by wheel traffic or animal trampling
  2. “Pan” or “transition layer” compaction – usually the result of tillage and present at the depth of the deepest tillage pass and/or near the transition from topsoil to subsoil
  3. Deep compaction – deeper than 12 inches, caused by either very high wheel loads, improper subsoiling or deep tillage, or in some cases natural consolidation

The focus here will be on pan compaction, which is quite common in Ontario soils.

Is subsoiling really necessary?

Compaction at this layer is not all bad. In fact, if it doesn’t excessively limit drainage, gas exchange, and root growth, some amount of subsurface compaction can actually be beneficial as it protects deeper subsoil layers from compaction that could be permanent. This is especially true in tilled fields where the topsoil can be loose and less effective in dissipating wheel loads, and in coarse to medium-fine textured soils (sandy, loamy, or silty soils with less than 18% clay content) where the subsoil structure is generally weaker and more vulnerable.

So how can you tell if compacted layers are “excessively” limiting? Measuring bulk density or soil hardness with a penetrometer won’t do, because the key is macro-porosity – large pores or channels. This is difficult to measure, so the best approach is to look at root development in a soil pit.

Reading Roots

Depending on the suspected depth of the problem (which can be estimated using a penetrometer), use a shovel or an excavator to dig a small pit across one or more crop rows. Clean any smearing from the side of the pit until you can start to see rooting patterns. Taking blocks of soil from the side of the pit in the compacted layer with a shovel and carefully breaking them open can also show if and how roots are growing, and whether there are macropores and root channels present.

Rooting patterns that indicate severe limitations include tap roots growing sideways, horizontal layering of roots, and roots deformed and/or thickened from trying to squeeze between large, compact soil structural units. Drainage limitations will create a “perched” water table indicated by gray soil colours and/or mottling. There will be fewer roots growing in the compacted layer, but if they are able to pass through and continue growing normally below the layer, subsoiling should not be necessary.

To see an example of this evaluation process, tune in to Ontario Virtual Diagnostic Days on September 14th.

Targeted disturbance

If pan compaction is severe enough and requires mechanical loosening, it must be done without compromising the load-bearing capacity of this layer that protects the deeper subsoil. In most cases, that means not completely breaking up and loosening the pan but creating cracks or fissures to re-establish vertical porosity for roots and water to pass through.

This can be achieved when the soil mass is lifted and flows over a subsurface blade, cracking as it bends (Figures 2, 3). A winged subsoiler tine is usually used for this operation, but the specifics of the setup are important.

Figure 2. Diagram showing tension cracks developed in soil flowing over a wing. (from Spoor, 2006)
Figure 2. Diagram showing tension cracks developed in soil flowing over a wing. (from Spoor, 2006)
Figure 3. Soil failure pattern created by a winged tine. Note the vertical fissures. (From Godwin and Spoor, 2015, after Spoor, 2006)
Figure 3. Soil failure pattern created by a winged tine. Note the vertical fissures. (From Godwin and Spoor, 2015, after Spoor, 2006)

 

 

 

 

 

 

 

 

 

 

 

With a winged subsoiler, the wing lift height (the vertical distance between the tip of the point and the upper edge of the wing) determines the degree of loosening and rearrangement. Too little lift won’t create enough tension to cause cracks, while too much will cause excessive disturbance. Working depth and soil moisture are also important factors. All else equal, greater working depths or higher soil moisture will result in fewer and smaller cracks. The target working depth should be just below the compacted layer, unless greater depth is required to produce the right type of disturbance.

Most subsoilers have multiple tines, and their spacing will also influence the result. If the compaction layer is consistent across the problem area, the complete soil mass should be uniformly lifted. Based on years of field work in the UK, Richard Godwin and Gordon Spoor recommend tine spacings between 1.5 and 2.0 times the working depth to achieve uniform lifting while leaving a level soil surface.

Is it worth it?

In severe cases, subsoiling can be the only way to remediate compaction in a reasonable timeframe for most farm operations. Done well, it can result in improved soil function and crop growth. But decades of research on subsoiling have shown mixed results. There are real risks of making the problem worse, and unless equipment traffic is controlled after subsoiling, re-compaction occurs quickly. When it comes to compaction, prevention is always the best solution. If that’s no longer possible, make sure you’re achieving your objectives for subsoiling, try to stabilize the newly created structure with roots, and avoid driving over it as long as possible.

Weather Data

Location Year Weekly August 2 – August 8 Accumulated
Highest Temp (°C) Lowest Temp (°C) Rain (mm) Rain (mm) April 1st GDD 0C April 1st  GDD 5C April 1st CHU May 1st
Harrow 2021 29 12 0 376 2210 1579 2290
2020 28 12 1 296 2124 1504 2298
2019 30 13 3 369 2066 1445 2128
Ridgetown 2021 29 9 1 363 2079 1455 2148
2020 28 11 32 298 2024 1420 2171
2019 28 11 62 504 1958 1339 2008
London 2021 28 11 1 305 2063 1446 2122
2020 27 12 64 312 1971 1369 2088
2019 28 13 9 427 1862 1267 1933
Brantford 2021 29 10 0 282 2033 1413 2074
2020 29 11 15 207 1988 1392 2076
2019 31 11   274 1929 1322 1991
Welland 2021 28 11 0 292 2034 1411 2093
2020 27 11 11 269 2020 1417 2174
2019 29 14 14 357 1996 1373 2088
Elora 2021 27 9 2 260 1881 1270 1924
2020 27 9 52 280 1824 1247 1940
2019 28 10 8 357 1512 974 1535
Mount Forest 2021 27 11 2 321 1887 1279 1943
2020 26 9 73 387 1799 1235 1948
2019 29 11   129 1740 1151 1822
Peterborough 2021 29 8 3 293 1879 1257 1904
2020 28 7 24 193 1814 1238 1912
2019 29 9 12 332 1725 1133 1734
Kingston 2021 28 12 0 211 1928 1307 1977
2020 29 11 29 263 1975 1367 2132
2019 28 12 29 336 1919 1300 1995
Kemptville 2021 31 12 1 240 2023 1395 2029
2020 29 11 40 220 1953 1356 2060
2019 31 8   203 1825 1229 1854
Earlton 2021 28 8 4 423 1744 1142 1730
2020 28 9 9 309 1626 1111 1785
2019 29 8 28 347 1445 926 1516
Sudbury 2021 27 8 15 317 1797 1195 1818
2020 27 9 17 361 1689 1150 1846
2019 28 8 28 350 1472 955 1550
Thunder Bay 2021 31 9 1 240 1653 1066 1667
2020 28 4 13 170 1508 999 1629
2019 28 10 6 264 1387 866 1439
Fort Frances 2021 31 10 0 186 1749 1156 1807
2020 27 3 6 207 1660 1113 1781
2019 30 7 21 292 1498 953 1550
Report compiled by OMAFRA using Environment Canada data. Data quality is verified but accuracy is not guaranteed. Report supplied for general information purposes only. An expanded report is available at www.fieldcropnews.com.