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Chapter 5a: Impact of fertilizers soil and
organic farming on nutritional value of plants
Sander van Delden
Horticulture and Product Physiology, WUR
 The dilution effect
 The effects of plant fertilizers on the nutritional value of plants for
humans per element:
● Calcium
● Potassium
● Iron
● Zinc
● Selenium
● Iodine
 Effect of soil health on the nutritional value of plants for humans
 Effect of Organic farming on the nutritional value of plants for
humans
2
Presentation Structure
Linking all the info
Organic
Matter
Structure
Drainage
Pathogens
Justus von
Liebig
“Yield is proportional to the amount of the
most limiting nutrient”
“Yield is proportional to the most limiting
growth factor”
 If all factors are optimal:
● Light
● Temperature
● Water and Nutrients
● Soil and Substrate
● Relative Humidity and Gas Exchange
● Phytohormones and plant volatiles
 There is optimal growth.
4
Dilution effect
5
Building blocks (elements) of
Production machinery
Vertical farming repairs the
barrel on all fronts
Vertical
farm
Optimal
CO2
H2O
Light
Minerals
Jarrell WM, Beverly RB. 1981. The Dilution Effect in Plant
Nutrition Studies In: Advances in agronomy. New York, 197–
224. DOI: 10.1016/S0065-2113(08)60887-1
The dilution Effect
High growth Lower mineral concentration
Also holds for many phytochemical
6
Example dilution effect: Increased CO2
Function and Facts on Calcium:
 Cell signalling
 Formation and stability of cell walls
 Membrane structure and permeability (turgor loss)
 Activation of some enzymes
 Big element 0.412 nm (hydrated)
7
Fertilizers and nutritional value: Calcium
Ca
Atom mass: 40 u
Atom no: 20
Plant uptake:
Ca2+
 Ca
2+
(± 0.5% of dry matter)
 Distribution via xylem (transpiration driven)
 Phloem seems to be unable to relocate Ca
8
Fertilizers and nutritional value: Calcium
Calcium excess can be toxic:
● Ca2+ neutralises excess of: Mg, K, P, Mn, Fe, B & Zn
● If low uptake of other elements is prevented Ca levels in
plant can increase without being toxic (upto 10 % of
DM).
High Mg, K, N  low uptake of Ca
 There is an interaction with nitrogen and calcium - though not
direct. When nitrogen is over applied to soil it will tend to bind
with calcium to form calcium nitrate and will leach calcium out.
In the plant high nitrogen pushes growth, but too quickly for
calcium to catch up and calcium deficiencies in the growing tip
are often the result.
9
Fertilizers and nutritional value: Calcium
10
Fertilizers and nutritional value: Calcium
Busse JS, Palta JP. 2006. Investigating
the in vivo calcium transport path to
developing potato tuber using 45Ca:
a new concept in potato tuber
calcium nutrition. Physiologia
Plantarum 128: 313–323. DOI:
10.1111/j.1399-3054.2006.00741.x.
 Plant calcium concentrations for optimal growth are e.g.:
● 2.5 μM monocot ryegrass
● 100 μM dicot tomato.
 40 fold difference caused by a different Ca demand, i.e.
● ryegrass needs 0.7 mg g kg-1
● tomato 12.9 g kg-1
 In general differences in Ca requirements between
species are explained by Ca2+-binding sites in the cell
walls, i.e. the cation-exchange capacity CEC (White and
Broadley 2003)
 Dayod et al. 2010 give a nice overview between plant
species
11
Fertilizers and nutritional value: Calcium
Dayod M, Tyerman SD, Leigh RA, Gilliham M. 2010.
Calcium storage in plants and the implications for calcium
biofortification. Protoplasma 247: 215–231. DOI:
10.1007/s00709-010-0182-0.
12
Fertilizers and nutritional value: Calcium
 Uptake is highly selective
 Very mobile in the plant
 Important in water relations
● And plant movement like leaf orientation
13
Fertilizers and nutritional value: Potassium
K
Atom mass: 39 u
Atom no: 19
Plant uptake:
K+
14
Fertilizers and nutritional value: Potassium
K
+
(± 1.0% of dry weight)
Key in plant water balances
Functioning of stomata
Cofactor in protein synthesis
Mobile
 Optimal plant growth is in the range of:
● 20–50 g K kg-1
dry mass
 Simply put:
● Low potassium, low overall nutritional status and
post-harvest quality.
● Especially fleshy fruits and tubers
 If growers want to increase plant organ K concentration this is simply
done by increasing K fertilization rate.
 Unfortunately, higher K fertilizer dose does not influence grain and
seeds K concentration this seems to be fixed on +/- 3 g kg-1.
 At high K supply rates ‘luxury consumption’ occurs, this deserves
attention as it can induce Mg and Ca deficiency symptoms.
15
Fertilizers and nutritional value: Potassium
Fertilizers and nutritional value: Iron
 Physiological function of iron:
● Iron is a component of cytochromes (mitochondrion, ATP
metabolism); activation of some enzymes
● Required for chlorophyll production and immobile
● hence lighter (white) young leaves
 Iron deficiency very common in lettuce and leafy greens in
general
 Availability issues by e.g.: high pH, broken chelates (UV),
unbalanced nutrient solutions
Fe
Atom mass: 55.8 u
Atom no: 26
Plant uptake:
Fe2+ & 3+
 Iron can be applied as ferrous sulfate or in a chelated form.
 Ferrous sulfate (FeSO4) contains about 20% iron.
● is inexpensive, mainly used for foliar spraying.
● Often ineffective in soils
 Iron chelates: Chelates stabilize metal ions and protect against
oxidation and precipitation.
 Iron chelates consist of three components:
● Fe3+ ions
● A complex, such as EDTA, DTPA, EDDHA, amino acids, humic-
fluivic acids, citrate.
● Sodium (Na+) or ammonium (NH4
+) ions

17
Fertilizers and nutritional value: Iron
 Different chelates hold iron ions in different strengths at different pH levels.
They also defer in their susceptibility to iron replacement by competitive ions.
For example, at high concentrations, calcium or magnesium ions may replace
the chelated metal ion.
18
Fertilizers and nutritional value: Iron
 Iron solubilization is required for plant uptake.
 Even in hydroculture where pH can be controlled,
aeration can lead to Fe oxidation, making it unavailable
for plant uptake.
 Chelates are organic molecules that help solubilize iron
19
Fertilizers and nutritional value: Iron
 Uptake in the form of Zn2+
● And at high pH ZnOH+
 Important in enzyme functioning and present in all six enzyme
classes: oxidoreductases, transferases, hydrolases, lyases,
isomerases and ligases.
● Hence Zn deficiency affects many aspects of plant
functioning. (Also photosynthesis)
 The critical deficiency concentrations <15–20 μg Zn g-1 dw
20
Fertilizers and nutritional value: Zinc
Zn
Atom mass: 65.3 u
Atom no: 30
Plant uptake:
Zn2+
 Zinc deficiency occurs in Overall low Zn level is:
● Low stress tolerance
● Low Pollen fertility => Low seed yield
● Low sugar content
● Lower phosphate as Zn is essential for P uptake
 Not mobile in plants
21
Fertilizers and nutritional value: Zinc
 Zn is essential for humans:
● 2800 proteins in the human proteome require Zn
 Strong binding of Zn to phytic acid =>
● Phytates reduce bioavailability of Zn
● Higher phytate concentration lower the
bioavailability of Zn and Fe
22
Fertilizers and nutritional value: Zinc
 Selenium is present in soil in small amounts:
● 0.01 to 2 mg kg⁻¹
 Chemically selenium (Se) has
commonalities with sulphur (S)
● Upregulated expression of sulphate transporters
leads to increase in selenate uptake
● Brassicaceae species accumulate more selenium
because they have a greater ability to accumulate
Sulphur
23
Fertilizers and nutritional value: Selenium
Se
Atom mass: 79 u
Atom no: 34
Plant uptake:
(H)SeOx
x-
24
Fertilizers and nutritional value: Selenium
Species Se concentration (mg kg-1 dw)
Astragalus pectinalus 4000 Accumulator
Stanleya pinnnata 330 Accumulator
Gutierrezia fremontii 70
Zea mays 10 Non Accumulator
Helianthus annuus 2 Non Accumulator
Selenium concentrations in shoots of accumulator and non-accumulator species
growing on a soil with 2–4 mg Se kg-1 (Copied from Marschner 2012)
Based on uptake plants are classified into Se-accumulators and
non-accumulators:
 Most agricultural and horticultural plant species are non-
accumulators
 White et al. (2007) found that Se non-accumulators had
a strong relationship between leaf S and leaf Se
concentration
 Transporter(s) of non-accumulators have a higher affinity
for sulphate than for selenate.
 Visa versa Se accumulators have a higher selectivity for
selenate than for sulphate.
25
Fertilizers and nutritional value: Selenium
Copied from Marschner 2012
 The high variation in Se soil content results in variation
of Se in the human diet.
 The minimum Se concentration for animals and humans
is about 50–100 μg Se kg-1 dw in fodder/food (Gissel-
Nielsen et al. 1984).
 Currently there are two strategies to increase human
intake of Se:
● using Se fertilizers: Agronomic biofortification
● Genetic biofortification by improvement in crop
Se accumulation.
26
Fertilizers and nutritional value: Selenium
 Agronomic biofortification
 Relatively easy to increase Se concentrations in food
crops by fertilization
● selenate is highly bioavailable to plants and is
readily transported from roots to shoots
● Se non accumulators can experience toxicity at high
Se fertilization
27
Fertilizers and nutritional value: Selenium
 Biofortification through classical breeding is hard:
● Requires genetic variation within the species
● In many species this no variation is found in Se uptake/assimilation
 Inter species variation is much bigger, as illustrated by the Se accumulators
(Table previous slide).
● Increase in Se uptake by transgenic plants overexpressing various
genes involved in S/Se assimilation.
● This was aimed to enhance Se uptake in Se-contaminated soils
(extremely high Se concentration)
● Unknown if these transgenic plants can accumulate more Se from soils
with low Se availability
28
Genetic Selenium biofortification
 Iodine is essential in human nutrition NOT for higher
plant species.
● billions of people have insufficient iodine intake
● lower plant species, including marine algae require
iodine as an essential element
 Iodine is not part of standard nutrient solutions in
horticulture nor of fertilization schemes in open field
agriculture
29
Fertilizers and nutritional value: Iodine
I
Atom mass: 127 u
Atom no: 53
Plant uptake:
I- and IO3
-
Best uptake
 Biofortification of vegetables with iodine can be used
to increase human iodine intake.
 Fertilization is a promising strategy for Iodine
biofortification concentration in edible plant parts
● Many studies found a significant increase upon
Iodine fertilization.
● Plant do not seem to be affected by additional
iodine in the nutrient solution. Growth is
comparable to “untreated” plants.
30
Fertilizers and nutritional value: Iodine
 All minerals we ingest originate from soils or substrates
and reach our bodies via the process of plants mineral
uptake (sometimes via animals).
 Not much research on the relation between soil health
and human health has been done.
31
Relation between soil health and the
nutritional value of plants for humans
 It is hard to isolate separate soil components in open
field agriculture.
● That is pot experiments and studies in artificial
environments can help, but effect are often
different from the reality in the field.
● In the field there are many confounding factors:
seasonal, location, soil condition, cultivar choice,
pest, disease, quality of sown seed
● all these factors can interact and together will
influence the outcome of the management
factors (treatment) applied
32
Scientific difficulties in relating soil health and
human health
 How does the factor organic matter influence nutritional value?
 Higher levels of organic matter increase:
● soil rooting capabilities,
● nutrient holding capacity,
● nutrient supply,
● aeration,
● water relations,
● self-cleaning capacity (i.e. breakdown of pesticides and
other toxic chemicals).
● reduces soil borne diseases by improving the resilience
and ecosystem complexity
 That seems good ! But is it too good?
33
Example of complexity: soil organic matter
 It can be that additional organic matter increases growth
so much that plant nutrient concentration is diluted.
 Too much organic matter can lead to slemping and
diseases. Or mineral toxicities.
 Effects of organic matter on poor sandy soil will be much
higher than on clay soils.
34
Example of complexity: soil organic matter
• The story of the
effects of tilling
on organic
matter content
 Three ways that soil health can impact human health:
i. Direct toxic effects such as radioactive or chemical contamination,
either naturally occurring or man-made
● E.g. high Cadmium levels in cheap P fertilizer
ii. Nutrient deficiencies or excesses
● Many ions can be supplied in excess to biofortify crops: e.g.
Zn, Fe, I, Se
● Soils can also contain low levels of these nutrients leading to
low content in the crop
iii. A general positive effect of soil health itself on plant and animal
health?
35
Relation between soil health and the
nutritional value of plants for humans
 Organic farming is not a clear cut “treatment” with a clearly
defined control “conventional farming”
● There is a lot of variability (soil, crops, management)
 On a policy level organic practices and regulations do not differ
substantially between countries
● Policy steers to organic as “chemical-free” farming
 Unfortunate as originally organic farming was conceived as a
holistic farming system aimed primarily at improving soil
health, and secondarily would lead to long term improvements
in animal, human, and societal health.
• (William A. Albrecht (1888–1974)
36
Organic farming and the nutritional value of
plants for humans
 Does the nutritional value of crops from organic farming differ
in nutritional value from conventional crops?
 NO: meta-analyses articles Dangour et al. (2009), Smith-
Spangler et al. (2012), Hoefkens et al. (2009)
● All show there are no significant composition differences
between organic and conventional crops.
 YES: meta-analyses articles Brandt and Mølgaard 2001;
Worthington 2001; Smith-Spangler et al. 2012; Barański et al.
2014
● Higher antioxidant/(poly)phenolics
● lower toxins like pesticides and cadmium
● lower concentrations of proteins, amino acids and fibre in
organic crops/crop-based compound foods
37
Ambiguity among research
38
 Organic farming has on average 20% lower yields and
higher yield fluctuation
 The higher stress resilience, higher antioxidants of
organic crops have benefits in post harvest
 Increase postharvest performance:
● potatoes with 17.7%, carrots 18.0%, turnips
15.7% and beets 29.4%.
 Thus, although the yield at harvest of organically grown
crops is lower, lower storage loss can compensate for
these losses.
39
Post harvest effect: Organic farming and the
nutritional value of plants for humans

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presentaties_wiki_teeltmaatregelen-groen_kennisnet_473051.pptx

  • 1. Chapter 5a: Impact of fertilizers soil and organic farming on nutritional value of plants Sander van Delden Horticulture and Product Physiology, WUR
  • 2.  The dilution effect  The effects of plant fertilizers on the nutritional value of plants for humans per element: ● Calcium ● Potassium ● Iron ● Zinc ● Selenium ● Iodine  Effect of soil health on the nutritional value of plants for humans  Effect of Organic farming on the nutritional value of plants for humans 2 Presentation Structure
  • 3. Linking all the info Organic Matter Structure Drainage Pathogens Justus von Liebig “Yield is proportional to the amount of the most limiting nutrient” “Yield is proportional to the most limiting growth factor”
  • 4.  If all factors are optimal: ● Light ● Temperature ● Water and Nutrients ● Soil and Substrate ● Relative Humidity and Gas Exchange ● Phytohormones and plant volatiles  There is optimal growth. 4 Dilution effect
  • 5. 5 Building blocks (elements) of Production machinery Vertical farming repairs the barrel on all fronts Vertical farm Optimal CO2 H2O Light Minerals Jarrell WM, Beverly RB. 1981. The Dilution Effect in Plant Nutrition Studies In: Advances in agronomy. New York, 197– 224. DOI: 10.1016/S0065-2113(08)60887-1 The dilution Effect High growth Lower mineral concentration Also holds for many phytochemical
  • 7. Function and Facts on Calcium:  Cell signalling  Formation and stability of cell walls  Membrane structure and permeability (turgor loss)  Activation of some enzymes  Big element 0.412 nm (hydrated) 7 Fertilizers and nutritional value: Calcium Ca Atom mass: 40 u Atom no: 20 Plant uptake: Ca2+
  • 8.  Ca 2+ (± 0.5% of dry matter)  Distribution via xylem (transpiration driven)  Phloem seems to be unable to relocate Ca 8 Fertilizers and nutritional value: Calcium
  • 9. Calcium excess can be toxic: ● Ca2+ neutralises excess of: Mg, K, P, Mn, Fe, B & Zn ● If low uptake of other elements is prevented Ca levels in plant can increase without being toxic (upto 10 % of DM). High Mg, K, N  low uptake of Ca  There is an interaction with nitrogen and calcium - though not direct. When nitrogen is over applied to soil it will tend to bind with calcium to form calcium nitrate and will leach calcium out. In the plant high nitrogen pushes growth, but too quickly for calcium to catch up and calcium deficiencies in the growing tip are often the result. 9 Fertilizers and nutritional value: Calcium
  • 10. 10 Fertilizers and nutritional value: Calcium Busse JS, Palta JP. 2006. Investigating the in vivo calcium transport path to developing potato tuber using 45Ca: a new concept in potato tuber calcium nutrition. Physiologia Plantarum 128: 313–323. DOI: 10.1111/j.1399-3054.2006.00741.x.
  • 11.  Plant calcium concentrations for optimal growth are e.g.: ● 2.5 μM monocot ryegrass ● 100 μM dicot tomato.  40 fold difference caused by a different Ca demand, i.e. ● ryegrass needs 0.7 mg g kg-1 ● tomato 12.9 g kg-1  In general differences in Ca requirements between species are explained by Ca2+-binding sites in the cell walls, i.e. the cation-exchange capacity CEC (White and Broadley 2003)  Dayod et al. 2010 give a nice overview between plant species 11 Fertilizers and nutritional value: Calcium Dayod M, Tyerman SD, Leigh RA, Gilliham M. 2010. Calcium storage in plants and the implications for calcium biofortification. Protoplasma 247: 215–231. DOI: 10.1007/s00709-010-0182-0.
  • 13.  Uptake is highly selective  Very mobile in the plant  Important in water relations ● And plant movement like leaf orientation 13 Fertilizers and nutritional value: Potassium K Atom mass: 39 u Atom no: 19 Plant uptake: K+
  • 14. 14 Fertilizers and nutritional value: Potassium K + (± 1.0% of dry weight) Key in plant water balances Functioning of stomata Cofactor in protein synthesis Mobile
  • 15.  Optimal plant growth is in the range of: ● 20–50 g K kg-1 dry mass  Simply put: ● Low potassium, low overall nutritional status and post-harvest quality. ● Especially fleshy fruits and tubers  If growers want to increase plant organ K concentration this is simply done by increasing K fertilization rate.  Unfortunately, higher K fertilizer dose does not influence grain and seeds K concentration this seems to be fixed on +/- 3 g kg-1.  At high K supply rates ‘luxury consumption’ occurs, this deserves attention as it can induce Mg and Ca deficiency symptoms. 15 Fertilizers and nutritional value: Potassium
  • 16. Fertilizers and nutritional value: Iron  Physiological function of iron: ● Iron is a component of cytochromes (mitochondrion, ATP metabolism); activation of some enzymes ● Required for chlorophyll production and immobile ● hence lighter (white) young leaves  Iron deficiency very common in lettuce and leafy greens in general  Availability issues by e.g.: high pH, broken chelates (UV), unbalanced nutrient solutions Fe Atom mass: 55.8 u Atom no: 26 Plant uptake: Fe2+ & 3+
  • 17.  Iron can be applied as ferrous sulfate or in a chelated form.  Ferrous sulfate (FeSO4) contains about 20% iron. ● is inexpensive, mainly used for foliar spraying. ● Often ineffective in soils  Iron chelates: Chelates stabilize metal ions and protect against oxidation and precipitation.  Iron chelates consist of three components: ● Fe3+ ions ● A complex, such as EDTA, DTPA, EDDHA, amino acids, humic- fluivic acids, citrate. ● Sodium (Na+) or ammonium (NH4 +) ions  17 Fertilizers and nutritional value: Iron
  • 18.  Different chelates hold iron ions in different strengths at different pH levels. They also defer in their susceptibility to iron replacement by competitive ions. For example, at high concentrations, calcium or magnesium ions may replace the chelated metal ion. 18 Fertilizers and nutritional value: Iron
  • 19.  Iron solubilization is required for plant uptake.  Even in hydroculture where pH can be controlled, aeration can lead to Fe oxidation, making it unavailable for plant uptake.  Chelates are organic molecules that help solubilize iron 19 Fertilizers and nutritional value: Iron
  • 20.  Uptake in the form of Zn2+ ● And at high pH ZnOH+  Important in enzyme functioning and present in all six enzyme classes: oxidoreductases, transferases, hydrolases, lyases, isomerases and ligases. ● Hence Zn deficiency affects many aspects of plant functioning. (Also photosynthesis)  The critical deficiency concentrations <15–20 μg Zn g-1 dw 20 Fertilizers and nutritional value: Zinc Zn Atom mass: 65.3 u Atom no: 30 Plant uptake: Zn2+
  • 21.  Zinc deficiency occurs in Overall low Zn level is: ● Low stress tolerance ● Low Pollen fertility => Low seed yield ● Low sugar content ● Lower phosphate as Zn is essential for P uptake  Not mobile in plants 21 Fertilizers and nutritional value: Zinc
  • 22.  Zn is essential for humans: ● 2800 proteins in the human proteome require Zn  Strong binding of Zn to phytic acid => ● Phytates reduce bioavailability of Zn ● Higher phytate concentration lower the bioavailability of Zn and Fe 22 Fertilizers and nutritional value: Zinc
  • 23.  Selenium is present in soil in small amounts: ● 0.01 to 2 mg kg⁻¹  Chemically selenium (Se) has commonalities with sulphur (S) ● Upregulated expression of sulphate transporters leads to increase in selenate uptake ● Brassicaceae species accumulate more selenium because they have a greater ability to accumulate Sulphur 23 Fertilizers and nutritional value: Selenium Se Atom mass: 79 u Atom no: 34 Plant uptake: (H)SeOx x-
  • 24. 24 Fertilizers and nutritional value: Selenium Species Se concentration (mg kg-1 dw) Astragalus pectinalus 4000 Accumulator Stanleya pinnnata 330 Accumulator Gutierrezia fremontii 70 Zea mays 10 Non Accumulator Helianthus annuus 2 Non Accumulator Selenium concentrations in shoots of accumulator and non-accumulator species growing on a soil with 2–4 mg Se kg-1 (Copied from Marschner 2012) Based on uptake plants are classified into Se-accumulators and non-accumulators:  Most agricultural and horticultural plant species are non- accumulators
  • 25.  White et al. (2007) found that Se non-accumulators had a strong relationship between leaf S and leaf Se concentration  Transporter(s) of non-accumulators have a higher affinity for sulphate than for selenate.  Visa versa Se accumulators have a higher selectivity for selenate than for sulphate. 25 Fertilizers and nutritional value: Selenium Copied from Marschner 2012
  • 26.  The high variation in Se soil content results in variation of Se in the human diet.  The minimum Se concentration for animals and humans is about 50–100 μg Se kg-1 dw in fodder/food (Gissel- Nielsen et al. 1984).  Currently there are two strategies to increase human intake of Se: ● using Se fertilizers: Agronomic biofortification ● Genetic biofortification by improvement in crop Se accumulation. 26 Fertilizers and nutritional value: Selenium
  • 27.  Agronomic biofortification  Relatively easy to increase Se concentrations in food crops by fertilization ● selenate is highly bioavailable to plants and is readily transported from roots to shoots ● Se non accumulators can experience toxicity at high Se fertilization 27 Fertilizers and nutritional value: Selenium
  • 28.  Biofortification through classical breeding is hard: ● Requires genetic variation within the species ● In many species this no variation is found in Se uptake/assimilation  Inter species variation is much bigger, as illustrated by the Se accumulators (Table previous slide). ● Increase in Se uptake by transgenic plants overexpressing various genes involved in S/Se assimilation. ● This was aimed to enhance Se uptake in Se-contaminated soils (extremely high Se concentration) ● Unknown if these transgenic plants can accumulate more Se from soils with low Se availability 28 Genetic Selenium biofortification
  • 29.  Iodine is essential in human nutrition NOT for higher plant species. ● billions of people have insufficient iodine intake ● lower plant species, including marine algae require iodine as an essential element  Iodine is not part of standard nutrient solutions in horticulture nor of fertilization schemes in open field agriculture 29 Fertilizers and nutritional value: Iodine I Atom mass: 127 u Atom no: 53 Plant uptake: I- and IO3 - Best uptake
  • 30.  Biofortification of vegetables with iodine can be used to increase human iodine intake.  Fertilization is a promising strategy for Iodine biofortification concentration in edible plant parts ● Many studies found a significant increase upon Iodine fertilization. ● Plant do not seem to be affected by additional iodine in the nutrient solution. Growth is comparable to “untreated” plants. 30 Fertilizers and nutritional value: Iodine
  • 31.  All minerals we ingest originate from soils or substrates and reach our bodies via the process of plants mineral uptake (sometimes via animals).  Not much research on the relation between soil health and human health has been done. 31 Relation between soil health and the nutritional value of plants for humans
  • 32.  It is hard to isolate separate soil components in open field agriculture. ● That is pot experiments and studies in artificial environments can help, but effect are often different from the reality in the field. ● In the field there are many confounding factors: seasonal, location, soil condition, cultivar choice, pest, disease, quality of sown seed ● all these factors can interact and together will influence the outcome of the management factors (treatment) applied 32 Scientific difficulties in relating soil health and human health
  • 33.  How does the factor organic matter influence nutritional value?  Higher levels of organic matter increase: ● soil rooting capabilities, ● nutrient holding capacity, ● nutrient supply, ● aeration, ● water relations, ● self-cleaning capacity (i.e. breakdown of pesticides and other toxic chemicals). ● reduces soil borne diseases by improving the resilience and ecosystem complexity  That seems good ! But is it too good? 33 Example of complexity: soil organic matter
  • 34.  It can be that additional organic matter increases growth so much that plant nutrient concentration is diluted.  Too much organic matter can lead to slemping and diseases. Or mineral toxicities.  Effects of organic matter on poor sandy soil will be much higher than on clay soils. 34 Example of complexity: soil organic matter • The story of the effects of tilling on organic matter content
  • 35.  Three ways that soil health can impact human health: i. Direct toxic effects such as radioactive or chemical contamination, either naturally occurring or man-made ● E.g. high Cadmium levels in cheap P fertilizer ii. Nutrient deficiencies or excesses ● Many ions can be supplied in excess to biofortify crops: e.g. Zn, Fe, I, Se ● Soils can also contain low levels of these nutrients leading to low content in the crop iii. A general positive effect of soil health itself on plant and animal health? 35 Relation between soil health and the nutritional value of plants for humans
  • 36.  Organic farming is not a clear cut “treatment” with a clearly defined control “conventional farming” ● There is a lot of variability (soil, crops, management)  On a policy level organic practices and regulations do not differ substantially between countries ● Policy steers to organic as “chemical-free” farming  Unfortunate as originally organic farming was conceived as a holistic farming system aimed primarily at improving soil health, and secondarily would lead to long term improvements in animal, human, and societal health. • (William A. Albrecht (1888–1974) 36 Organic farming and the nutritional value of plants for humans
  • 37.  Does the nutritional value of crops from organic farming differ in nutritional value from conventional crops?  NO: meta-analyses articles Dangour et al. (2009), Smith- Spangler et al. (2012), Hoefkens et al. (2009) ● All show there are no significant composition differences between organic and conventional crops.  YES: meta-analyses articles Brandt and Mølgaard 2001; Worthington 2001; Smith-Spangler et al. 2012; Barański et al. 2014 ● Higher antioxidant/(poly)phenolics ● lower toxins like pesticides and cadmium ● lower concentrations of proteins, amino acids and fibre in organic crops/crop-based compound foods 37 Ambiguity among research
  • 38. 38
  • 39.  Organic farming has on average 20% lower yields and higher yield fluctuation  The higher stress resilience, higher antioxidants of organic crops have benefits in post harvest  Increase postharvest performance: ● potatoes with 17.7%, carrots 18.0%, turnips 15.7% and beets 29.4%.  Thus, although the yield at harvest of organically grown crops is lower, lower storage loss can compensate for these losses. 39 Post harvest effect: Organic farming and the nutritional value of plants for humans

Editor's Notes

  1. Picture taken from: https://homeandgardenlawncare.com/understanding-numbers-in-a-fertilizer-bag/
  2. : Copied from Loladze (2014): the effect of CO2 on individual chemical elements in plants. Change (%) in the mean concentration of chemical elements in plants grown in eCO2 relative to those grown at ambient levels. Unless noted otherwise, all results in this and subsequent figures are for C3 plants. Average ambient and elevated CO2 levels across all the studies are 368 ppm and 689 ppm respectively. The results reflect the plant data (foliar and edible tissues, FACE and non-FACE studies) from four continents. Error bars represent the standard error of the mean (calculated using the number of mean observations for each element). The number of mean and total (with all the replicates) observations for each element is as follows: C(35/169), N(140/696), P(152/836), K(128/605), Ca(139/739), S(67/373), Mg(123/650), Fe(125/639), Zn(123/702), Cu(124/612), and Mn(101/493). An element is shown individually if the statistical power for a 5% effect size for the element is >0.40. The ‘ionome’ bar reflects all the data on 25 minerals (all the elements in the dataset except of C and N). All the data are available at Dryad depository and at GitHub.
  3. Excess calcium is just as bad as having not enough! Ca2+ neutralises excess of: Mg, K, P, Mn, Fe, B & Zn High Mg, K, N  low uptake of Ca Gives resistance against fungal attacks (important in disease management!) There is an interaction with nitrogen and calcium - though not direct. When nitrogen is over applied to soil it will tend to bind with calcium to form calcium nitrate and will leach calcium out. In the plant high nitrogen pushes growth, but too quickly for calcium to catch up and calcium deficiencies in the growing tip is often the result. Calcium plays a key (the cementing layer between the cell walls of adjacent plant cells). Calcium ions (Ca2) are also important in a number of physiological roles in plants, such as altering membrane permeability and cell
  4. Excess calcium is just as bad as having not enough! Ca2+ neutralises excess of: Mg, K, P, Mn, Fe, B & Zn High Mg, K, N  low uptake of Ca Gives resistance against fungal attacks (important in disease management!) There is an interaction with nitrogen and calcium - though not direct. When nitrogen is over applied to soil it will tend to bind with calcium to form calcium nitrate and will leach calcium out. In the plant high nitrogen pushes growth, but too quickly for calcium to catch up and calcium deficiencies in the growing tip is often the result. Calcium plays a key (the cementing layer between the cell walls of adjacent plant cells). Calcium ions (Ca2) are also important in a number of physiological roles in plants, such as altering membrane permeability and cell
  5. Excess calcium is just as bad as having not enough! Ca2+ neutralises excess of: Mg, K, P, Mn, Fe, B & Zn High Mg, K, N  low uptake of Ca Gives resistance against fungal attacks (important in disease management!) There is an interaction with nitrogen and calcium - though not direct. When nitrogen is over applied to soil it will tend to bind with calcium to form calcium nitrate and will leach calcium out. In the plant high nitrogen pushes growth, but too quickly for calcium to catch up and calcium deficiencies in the growing tip is often the result. Calcium plays a key (the cementing layer between the cell walls of adjacent plant cells). Calcium ions (Ca2) are also important in a number of physiological roles in plants, such as altering membrane permeability and cell
  6. The radioactive signal exactly overlapped the water transport pathway in the tuber marked with Safranin O dye, suggesting that water and calcium can be simultaneously transported from stolon roots to the tuber. No transport of 45Ca across the tuber periderm was detected 8 days after 45Ca was applied to the tuber periderm. This indicated that no significant transport of calcium occurs from the soil across the periderm. Our results provide evidence that: (1) calcium is not re-translocated via the phloem from the aerial shoot tubers and main (basal) roots; (2) the main root system does not supply calcium to the tuber; (3) calcium is not transported across the periderm to the interior tuber tissue; (4) calcium is transported to the tuber via the xylem along with water, and the roots on the stolon associated with the tuber supply water and calcium to the developing tuber; and (5) transpirational demand is a significant determinant of calcium distribution within the plant. Introduction
  7. Dayod M, Tyerman SD, Leigh RA, Gilliham M. 2010. Calcium storage in plants and the implications for calcium biofortification. Protoplasma 247: 215–231. DOI: 10.1007/s00709-010-0182-0.
  8. http://farmextensionmanager.com/English/Coffee%20technology%20bank/pest%20doctor/Potassium%20Deficiency.html Bladrand Symptoms look like water deficiency
  9. Some examples of processes were K is important.
  10. pH above 7.0, because its iron quickly transforms to Fe3+ and precipitates as one of the iron oxides.
  11. Fe-EDTA - This iron chelate is stable at pH below 6.0. Above pH of 6.5, nearly 50% of the iron is unavailable. Therefore this chelate is ineffective in alkaline soils. This chelate also has high affinity to calcium, so it is advised not to use it in calcium-rich soils or water.  Note that EDTA is a very stable chelate of micro-elements, other than iron, even in high pH levels. Fe-DTPA - this iron chelate is stable in pH levels of up to 7.0, and is not as susceptible to iron replacement by calcium.   Fe-EDDHA - this chelate is stable at pH levels as high as 11.0, but it is also the most expensive iron chelate available. In soilless media and hydroponics, pH monitoring of water and media is relatively easier than in soils. When regular testing is performed, and pH control is adequate, it is possible to prefer the inexpensive, less stable iron chelates. On the other hand, in alkaline soils, where it is difficult to effectively decrease pH levels, it is advised to use more stable iron chelates, such as EDDHA. http://www.horticoop.nl/Home/Gewasbeschermingmeststoffen/Meststoffen/IJzerchelaten/tabid/426/Default.aspx http://www.relabdenhaan.com/UserData/Documents/4E790AD8FF87491EB169127BEC361383.pdf Mn EDTA 3 – 10 Zn EDTA 2 – 10 Cu EDTA 1.5 – 10 Ca EDTA 5 – 10 Mg EDTA 6 – 10 Fe-EDTA - This iron chelate is stable at pH below 6.0. Above pH of 6.5, nearly 50% of the iron is unavailable. Therefore this chelate is ineffective in alkaline soils. This chelate also has high affinity to calcium, so it is advised not to use it in calcium-rich soils or water. 
  12. Based on differences in Se content plants can be classified into Se-accumulators and non-accumulators
  13. Photo: https://nl.123rf.com/stock-foto/57560247.html?oriSearch=image+id+++57560247&sti=nw3473mzb2cnof7d9v|&mediapopup=57610757
  14. Photo: https://www.agweb.com/article/soil-health-you-can-build-organic-matter-naa-darrell-smith/
  15. Another example of relating soil health to human health in research is the effect of tilling. Tilling is a management practice that is generally thought to reduce the amount of soil organic matter. That is by the additional aeriation and partipitation soil live will increase organic matter consumption. Although this is in many cases really the case, one must consider that tilling itself reduces the soil density directly, i.e. creating more pores and aeration, thereby increasing the volume per unit of mass. As organic matter is often measured by taking a certain soil volume, it is inevitable that directly after tilling soil organic matter seems to be reduced. Per area of land however, nothing has changed (Figure 5.9). Teasdale et al. (2007) provide another example of this complexity. They showed that even when organic matter is measured correctly, then still there are very contrasting results on this topic. In their study they compared 9 years of conventional no-tillage management to organic management. Their results show organic agriculture has greater long-term soil improvement and organic matter content than conventional agriculture, despite the use of tillage. That is because organic practices include cover crops, crop rotation and application of livestock manure. In the Netherlands many farmers use cover crops, animal manure, compost, crop rotation on conventional farms. This is one of the reasons why organic matter in the Netherlands is not declining as hard as in other parts of the World. However, stricter regulations on usage of animal manure might be a real cause of concern (Rotgers 2008). That is, farmers can only use the “excess” of manure that comes from our livestock industry to a certain extent, because of phosphate regulations. To maintain high yields the farmers resort to the use artificial fertilizers, many of which contain only macronutrients and no organic matter. On the long term this will significantly reduce micro nutrient content in plants, which might have its impact on the livestock and human diet as well. Figure 5.9: Tillage-induced changes in soil horizonation, bulk density and mass: tillage increases the thickness per unit area (i.e. volume) occupied by the same mass of soil and organic, thus misinterpretations are inevitable for calculations based on the fixed 0- to 150 mm layer (indicated by the double arrow) and quite likely for calculations based on identification of the boundary between the Ap and B horizons. (Copied from Ellertl and Bettany 1995).
  16. The most recent study by Baranski et al (2014) point out that the main reason for the inability of previous studies to detect composition differences was probably the limited number of datasets available or included in analyses by these authors, which would have decreased the statistical power of the meta-analyses. Other reasons for the disagreements can be traced to whether nutrient content was measured on a dry matter or fresh weight basis. Organic foods are generally higher in dry matter content, therefore it is very likely that the actual consumed fresh weight is higher in nutrient content. However, when measured on a dry weight basis differences will not be detected. Another factor that makes it hard to relate organic practices to human health effects is the fact that human nutritionists have not reached a consensus on what the actual beneficial phytochemicals in fruit and vegetables are (see Chapter 2).
  17. Results of the standard unweighted and weighted meta-analyses for antioxidant activity, plant secondary metabolites with antioxidant activity, macronutrients, nitrogen compounds and cadmium (data reported for all crops and crop-based foods included in the same analysis). MPD, mean percentage difference; CONV, conventional food samples; ORG, organic food samples; n, number of data points included in the meta-analyses; FRAP, ferric reducing antioxidant potential; ORAC, oxygen radical absorbance capacity; TEAC, Trolox equivalent antioxidant capacity; SMD, standardised mean difference. Values are standardised mean differences, with 95 % confidence intervals represented by horizontal bars. * P value < 0.05 indicates a significant difference between ORG and CONV.†Numerical values for MPD; ‡Ln ratio = Ln(ORG/CONV £ 100 %). §Hetero-geneity and the /2 statistic. || Data reported for different compounds within the same chemical group were included in the same meta-analyses. ¶ Outlying data points (where the MPD between ORG and CONV was more than fifty times greater than the mean value including the outliers) were removed. , MPD calculated using data included in the standard unweighted meta-analysis; , MPD calculated using data included in the standard weighted meta-analysis;  SMD.