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Soil data

questions

  • Is there a statistically significant difference in the a) organic matter content, b) nutrient content, and c) compaction of soils between dig, no-dig and uncultivated plot types? (i.e. Is there a difference which is not due to chance?)
  • Are there signs of nutrient leaching to depths below the root zone? For this we compared cultivated and non-cultivated soils below 30 cm depth?
  • Is there a tendency for any particular nutrient to be deficient?

organic matter

The mean percentage organic matter content by mass for the 2-9 cm root zone of dig, no dig and uncultivated plots are 10.01%, 23.89% and 13.17% respectively. However, these figures are skewed by unusually high values at Springhill Community Garden. This was due to the site having new no-dig, raised beds full of fresh compost. The organic matter content of these beds was up to 88.52% in the 2-9 cm layer. It can therefore be more meaningful to look at median (mid) values for each category. Median values are 9.89%, 14.03% and 13.13% respectively.

Figure 1: Median percentage organic matter by depth and ground type

Figure 1 shows that no-dig beds tend to hold more organic matter than the dig plots in the upper soil layer. This is even after the top 2 cm of soil was discarded to eliminate areas of high variability.

organic carbon

Soil organic carbon can be approximately calculated by dividing the soil organic matter content by 1.72. This is based on the common assumption that organic carbon makes up 58% of organic matter. If it is assumed that the organic matter content of the top 10 cm of soil is uniform based on the 2-9 cm measurements, the quantity of organic carbon in the top soil can be calculated in kilograms per metre square (kg OC/m2) or can be scaled up to tonnes per hectare (t OC/ha) to be more comparable to farm land.

This calculation considers the bulk density of the soil which narrows the range compared to percentage organic matter, as highly organic soil generally have a lower bulk density. ANOVA was applied to the organic carbon content of the three land types (dig, no-dig, uncultivated), finding a significant difference between the groups (p = 0.001).

The figures upscaled to t OC/ha are 35.31, 44.48, and 44.05 for dig, no-dig and uncultivated respectively.

Figure 2: kg of organic carbon per metre square by ground type. (Error bars show standard deviation from the mean.)

nitrogen

Figure 3: Median nitrate levels by ground type at different depths
Figure 4: Median ammonium levels by ground type at different depths

potassium

A Kruskal-Wallis tests found that levels of potassium (K) in the soils were not significantly different between dig, no-dig and uncultivated areas at any depth when all 3 ground types were considered. The highest levels were found in the surface layer of dig beds. However, the median K concentration in no-dig beds remained reasonably consistent through the deeper soil and was higher than dig or uncultivated areas at 15-22 cm and 30+ cm.

Of the 199 samples, 73 were considered “very low” or “low”, while 79 were considered “moderate-” or “moderate+”. A total of 47 were considered “high” or “very high”.

Figure 5: Median potassium levels by area type at different depths

phosphorus

There was a significant difference in phosphorus levels between ground type in the 2-9 cm soil layer (p=0.03). This was largely due to the difference between the cultivated and uncultivated areas. If the uncultivated are excluded, there is no significant difference between dig and no-dig plots (p=0.68). The significance of the mid-depth group was borderline with a p-value of 0.07.

From a total of 199 separate samples, 177 were considered to have “very high” levels, with a further 15 in the “high” category according to the descriptive SAC nutrient index.

Figure 6: Median phosphorus levels by area type at different depths

calcium

Calcium levels were not significantly different between dig, no-dig and uncultivated land at any depth. P-values generated by Kruskal-Wallis tests in for 2-9 cm, 15-22 cm and 30+ cm were 0.54, 0.10 and 0.77 respectively.

Calcium levels are related to the pH of the soil, with lower levels associated with lower pH. Excessive quantities can prevent other positively charged nutrients from binding to the soil.

Figure 7: Median calcium levels by ground type at different depths

magnesium

Soil magnesium levels were generally higher in no-dig soils. The difference was not statistically significant between ground types at depths of 15-22 cm or 30+cm. At 2-9 cm the significance was borderline (p=0.06).

82 of 199 samples were considered to be “very low” or “low” in magnesium, with 96 in the “moderate” category. No samples were considered to be “very high”.

Figure 8: Median magnesium levels by ground type at different depths

interpretation

Figure 9: Key to SAC nutrient status extracted from the Potash Development Association

correlations between soil properties

The maximum possible correlation value is 1.0, which would indicate 100% alignment between two variables. Figure 9 below shows that our highest correlation value was 0.71, which was between calcium and phosphorus levels. The second highest correlation was between bulk density and organic matter content. As organic matter generally has a low density, a high correlation value is expected.

Figure 10: Correlations between different soil properties

soil compaction

Soil compaction was measured with a penetrometer with approximately 12 measurements at each site on each different ground type. Figure 11 shows the mean value for each depths for all the sites combined. It can be seen that uncultivated ground is more compact at all depths than cultivated ground, as may be expected. Values greater than 2000 kPa are highly restrictive to root growth. These mostly occurred in uncultivated ground with none in the main 2-9 cm root zone of cultivated areas.

Figure 11: Soil compaction for different ground types

Links to free literature

This study was funded and supported by EASTBIO Doctoral Partnership (by BBSRC), the University of Aberdeen and the University of Edinburgh

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Disclaimer: The funders have no responsibility for the information provided or views expressed in this website. The views expressed are solely those of the author.

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