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Table 2 Summary of P-NMR results from selected studies

From: Characterizing phosphorus forms in cropland soils with solution 31P-NMR: past studies and future research needs

Location

Madagascar [48]

China [54]

Sweden [60]

Switzerland [61]

Canada [65]

Brazil [75]

Crop

Rice

Greenhouse, double-crop tomatoes

Grain-based rotation

8-year, wheat-based rotation

Continuous monoculture wheat

Various summer crops, winter cover crop

Fertilizers

Different rice cropping systems; CF, AM, COM

CF, AM; high N fertilizer, leaching

Soil textures, fertilization rates (CF, AM)

Fertilization; 0, CF, AM, COM, SS; EH

Long-term with and without CF

Grazed and ungrazed winter cover crops, CF

Soil pH

4.64–5.82a

6.91–7.03

5.8–7.5

4.8–5.9

5.4–6.6

5.2–6.4

Total P (mg kg−1)

133–1378

685–2446

288–980

442–1150

440–615

841–2531

Soil test P (mg kg−1)b

<1–6.9 (O)

20–210 (O)

179–1128 (M)

12–223 (A)

114–58 (R)

3–33 (O)

21–103 (M)

22–71 (M)

P recovery (%)c

36–82

49–74

48–98

73–96

36–50

60–88

OrthoP (%)d

54–80

90.7–93.4

20.4–75.7

53–80

22.6–44.1

71.6–77.6

Pyro P (%)

0–4

0.3–0.8

0–3.2

0.3–0.5

1.0–1.4

2.0–2.3

Myo-IHP (%)

0–5

0.5–1.7

0–24

3.0–6.6

4.6–8.5

6.5–9.7

Scyllo-IHP (%)

0–4

0.1–0.3

1.4–6.6

1.0–2.7

0.8–2.7

2.9–3.9

Other mono (%)

nde

4.2–8.4

nd

7.3–12.2

29.3–34.2

0.7–1.1

DNA (%)

0–9

0.0–2.0

0–3

0

0.3–1.2

0.3–1.6

Other diesters (%)f

nd

0.0–0.7

0–17.5

0.7–1.1

2.8–4.5

6.8–9.8

cM:Dg

nd

1.5–2.0

0.9–5.6

16–25

1.2–1.5

1.3–1.5

  1. AM animal manure, CF chemical fertilizer, COM compost, EA measured phosphomonoesterase and phosphodiesterase activities, EH enzyme hydrolysis, RW recycled wastewater, SS sewage sludge, please see the original publications for more details
  2. aRange for all depths and treatments
  3. bSoil test P: A, ammonium lactate; M, Mehlich; O, Olsen; R, Resin
  4. cPercentage of total P extracted in NaOH–EDTA
  5. dPercentage of spectral area
  6. eCould not be determined from information in the publication
  7. fCalculated from information for α- and β-glycerophosphate and nucleotides as given in paper, if not already calculated in the paper
  8. gCorrected for diester degradation compounds