Future research

The approach used in the present study to associate a set of visual observations to the soils’ potential to function, enabled fair comparison of soil quality between sites with different soil properties. The stepwise linear regression approach showed potential to design scoring functions to evaluate various soil functions based on (quantitative) visual observations, which can be easily repeated to other geographic areas if data is available. Another reproducible approach was presented by Pulido Moncada et al.

(2014), who used classification and regression trees to identify associations between soil chemical and physical properties. Data in classification and regression trees, however, is grouped based on the distribution of the data, rather than that those identified groups of data correlate with soil functions. A stepwise linear regression approach is than preferred, as it results in direct correlations between visual observations and soil functions.

Despite the fact that the stepwise linear regression approach showed potential to assess various soil functions, the stepwise linear regression models found in this study are not readily applicable to other areas, because they are based on rather small set of observations with site-specific soil properties (Table A.4.9 and A.4.10). For use of these methods elsewhere, we recommend to collect more visual soil observations together with quantified soil function indicators, to make the regression models more robust.

A major challenge of the method used in the present paper was that the laboratory measurements of the soil moisture retention characteristics (needed to quantify the modelled soil function indicators) were time consuming. A solution could be to go to sites where data of soil hydraulic properties and/or soil moisture retention characteristics are available, to be used to quantify soil function indicators. Databases are available, such as BOFEK in the Netherlands (Wösten et al., 2013), or Hypres in Europe (Wösten, 2000). Also, it is possible to use less complex versions of SWAP, or to use other soil hydrological models than SWAP, such as Hydrus1D (Šimůnek et al., n.d.) or MACRO (Larsbo and Jarvis, 2003). More quantitative visual soil observations allow analyses of optima and nonlinear relationships between quantitative visual observations and soil function indicators, as well as interactions with soil texture.

Furthermore, the addition of soil chemical data next to collected quantitative visual soil observations could be helpful to understand the broader context of soil functioning and the environmental performance of agricultural land.

4.5 Conclusions

Quantitative visual soil evaluation were used to assess a range of soil functions for dairy farmed soils in the Netherlands. Soil function indicators showed stronger correlations with a set of quantitative visual soil observations, than with single quantitative visual observation. Stepwise linear regression analysis showed that quantitative visual observations associated with the following soil function indicators:

measured plant available water and water storage capacity; modelled yield gaps for a wet year (2001), a dry year (2003), and a ‘normal’ year (2016); and oxygen stress for a wet year (2001). Those quantified soil function indicators were based on soil physical properties, and therefore they could be associated with a set of quantitative visual soil observations that also focus on soil physical properties. Measured nitrate and phosphate concentrations in ground- and surface water also associated with a set of quantitative visual observations. This is attributed to correlations between soil physical properties and soil chemical properties, climate and management. For several soil function indicators, the association with a set of quantitative visual observations was affected by soil texture. This shows the importance of evaluating soil quality in relation to the soils’ potential to function, which can vary between soil types. Also, in the present study not all soil function indicators were optimal at the same time. For instance, a high water storage capacity was associated with high nitrate concentrations, and low yield gaps in a wet year were also associated with high nitrate concentrations. This study showed that visual soil evaluations can assess several soil functions at the same time, to be able to assess and evaluate soil quality in relation to environmental performance of agricultural land.

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Appendix 4 ble A.4.7. Overview of used groundwater table data or free drainage assumptions at the sampled fields. This table continues on the next pag FarmFieldsFree drainage assumption

Groundwatertable monthlymeans (cm below surface) Data originEnd measurements HighestLowest 1 1-5 Yes 150 300 DINOloket B34C0044; B34C0150; B34C0159; B34C0213 2 1, 3 No 105 (Feb. 2017)1 153 (Oct. 2016)1 Measured 1 27/02/171 2, 4, 5Yes 3 2 Yes 214 (Aug. 2016)271 - piezometer often dry Measured 27/02/17 3 Yes 193 (Aug. 2016)266 - piezometer often dry Measured 27/02/17 5 No 99 (Feb. 2016)158 (Oct. 2016)DINOloket B33E1281 1, 4 No 133 (Jan./Feb. 2001-2003)232 (Jul./Sep.-Oct. 2001-2003)DINOloket 33F0247 (2001-2003) 4 1, 3 No 42 (Mar. 2017) 159 (Oct. 2016)Measured 10/04/17 4 No 49 (Mar. 2017)145 (Oct. 2016)Measured 7/04/17 3 No 56 (Feb. 2016)147 (Oct. 2016)DINOloket B07B0141 (2016-2017) 5 No 66 (Feb. 2016)144 (Oct. 2016)DINOloket B07B1166 (2016-2017)

1 On Farm 2 the diver that measured the air pressure, inadvertently stopped after one month of measurements, and daily mean air pressure records were used from a nearby weather station (17 km, Table A.4.8), and calibrated to replace and complement the diver records (estimated local air pressure = 0.918 * Twenthe air pressure + 93.242, R2=0.86 for the 30-day overlap). Table A.4.8. Daily mean weather records obtained from KNMI weather and precipitation stations. FarmPrecipitation station name (KNMI reference number)

Distance from farm (km) Weather stationDistance from farm (km) 1 Hengelo (654) 3 Hupsel (283)10 2 Tubbergen (361) 7 Twenthe (290) 17 3 Almen (678) 9 Deelen (275) 25 Apeldoorn (543) 9 Deelen (275) 20 4 Ezinge (136) 9 Eelde (280) 18.5 5 Geldermalsen (584) 5 Herwijnen (356) 9

5 1, 3, 4, 5No 87 (Mar. 2017)112 (Dec. 2016) Measured 7/04/17 2 No 112 (Jan./Feb. 2001- 2003) 195 (Jul./Aug./Sep. 2001-2003)DINOloket B39C0211 (2001- 2003)

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Table A.4.9. Average and standard deviations of all quantitative visual observations. Grass cover (%) Biopore (count) Root (count) Munsell soil colour value (dark=2, lighter>2) Gley (%) Soil structure (VSA score: 2=good; 0=bad) Fraction largest soil structural elements (%) Earth- worm (count)

Depth compacted layer (cm below surface) Number of observations202322252525252525 Average595 187 2.6 6 0.9 631414 Standard deviation 225 134 0.7 8 0.4 231611 Degree of soil compaction (VSAscore: 2=good; 0=bad)

Depth of 85% ofroots (cm below surface) DepthA horizon (cmbelow surface) Mean highest groundwater table (cm below surface) Maximum rooting depth (cmbelow surface)

Soilorganic matter content (fraction) Number of observations252525252525 Average0.7 293546980.068 Standard deviation 0.4 9 1351350.033

Table A.4.10. Average and standard deviations of soil functions. Plant available water (cm3 cm-3) Water storage capacity (cm3 cm-3) Yield gap 2016 (%) Yield gap 2001 (%) Yield gap 2003 (%) Relative oxygen stress 2001 (%) Relative drought stress 2003 (%) Nitrate concentration (mg L-1 )

Phosphate concentration (mg L-1 ) Number of observations252525252525251515 Average0.180.090.100.120.120.040.0633.40.03 Standard deviation 0.040.050.120.160.11 0.050.0427.30.02

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Table A.4.11. Ramsey’s RESET test shows that quadratic and/or interaction terms would not improve the regression models, because P>0.05.

Soil function P-value

Plant available water 0.82 Water storage capacity 0.97

Yield gap 2016 0.84

Yield gap 2001 0.87

Yield gap 2003 0.83

Relative oxygen stress 2001 0.60 Relative drought stress 2003 NA Nitrate concentration 0.94 Phosphate concentration NA

Chapter 4

Chapter 5

Synthesis