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Research ArticleOpen Access

Soil pH, Ca and Mg Stability and pH Association with Temperature and Groundwater Silicon Volume 1 - Issue 7

Timo Töysä*1 and Osmo Hänninen2

  • 1Specialty General Practice, Rehabilitation Hospital Vetrea, Finland
  • 2Department of Physiology, University of Eastern Finland, Finland

Received: November 16, 2017;   Published: December 04, 2017

Corresponding author: Timo Töysä, Specialty General Practice, Rehabilitation Hospital Vetrea, Pohjolankatu 15, FI-74100 Iisalmi

DOI: 10.26717/BJSTR.2017.01.000564

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Abstract

Objective: It is generally known that pH, Ca and Mg have changed remarkably during 1961-90, but their inter-areal variation seems not have been fully discussed nor explained. Parameters of cropland have been earlier associated with CHD mortality. Silicon (Si) and temperature (Temp) have been earlier assessed with human CHD mortality. In this study we have assessed soil values of 21 Rural Centers (RC) from the 1960’s, 1970’s and 1980’s, [(60’s) (70’s), (80’s)] with respective mean annual temperatures from 1981-2010 and mean groundwater (gw) Si content.

Results: Combined regression by pH(60’s) and pH(70’s) explained pH(80) by 96.8 % (p < 0.001). Ca. (60’s) and Ca.(70’s) explained respectively Ca.(80’s) by 99.3 % (p < 0.001) and Mg.(60’s) and Mg.(70’s) explained respectively Mg.(80’s) by 92.3 % (p < 0.001). Combined regression by Temp and Si explained pH (80’s) by 86.5 % (p < 0.001). Respectively combined regression by Temp and pH (80’s) explained gw Si by 77.5 % (p < 0.001).

Conclusion: Groundwater silicon is associated with the soil matrix factor (sources of groundwater silicon/silicon colloids?), which seems with temperature to explain inter-areal pH variation and obviously is associated with relative local stability of cropland Ca and Mg (and soil fertility). Maybe now is the time to increase Si trials in agriculture.

Abbreviations: RC : Rural Centers; FMI: Finnish Meteorological Institute; ETS: Effective Temperature Sum

Introduction

It is generally known that pH, Ca and Mg have changed remarkably during 1961-90 [1,2,3] but their inter-areal variation seems not have been fully discussed nor explained. Parameters of cropland have been earlier associated with CHD mortality [4]. In this survey based on old statistics has been discovered great stability in inter-RC soil parameters and connection of this stability with temperature and gw Si.

Material and Methods

Soil data is from Eurofins Viljavuuspalvelu as in our earlier publications [1-4]. The soil values [1-3] given as 5 year periods (1961-65, 1966-70,..) were combined to decade periods [(60’s), (70’s), (80’s)]. Values of “(9).Kymenlaakso” and “(10).Etelä- Karjala” were combined to”(9;10).Kymi” by weighting the soil values by their cropland areas in 1988 (4,5). Respectively values of “(17).Keski-Pohjanmaan” and “(18).Oulun” were combined to “(17;18).K-Pohjanmaan, Oulun” and used as such in statistics. Available provincial Si.gw.m data from Geologic Survey of Finland [5] have been changed to approximate RC values by its provincial values as such if RC was totally inside of the province, in other cases by weighting the different Si.gw.w values of different provinces by their cropland areas. Area weights selected for this study as earlier from 1988 [4,5]. The values of RC temperatures were determined by benefiting the map of RCs in Official Statistics of Finland [6] and the map of Finnish Meteorological Institute (FMI) [7], by selecting their central commune and then visually estimating its place between the temperature lines.

Results

Table 1 shows that the range of periodical changes varied between 5.4 (pH) and 15.8 % (Ca).

Table 1: Changes of the mean RC soil values between the 1960’s and 1980’s.

Combined regression by pH (60’s) and pH (70’s) explained pH (80’s) by 96.8 % (p < 0.001).

Combined regression by Ca. (60’s) and Ca. (70’s) explained Ca. (80’s) by 99.3 % (p < 0.001)

Combined regression by Mg. (60’s) and Mg. (70’s) explained Mg. (80’s) by 92.3 % (p < 0.001)

Combined regression by Temp and Si explained pH.(80’s) by 86.5 % (p < 0.001). (Fig.1)

Computation gave equation: pH [Temp; Si (mg/L)] = 6.02 + 0.16*Temp - 0.11*Si (mg/L).

Combined regression by Temp and pH (80’s) explained Si by 77.5 % (p < 0.001):

Computation gave equation: Si (mg/L) = 38.5 + 1.14*Temp - 6.12* pH.

Discussion

Values (60’s) and (70’s) explained inter-RC variations (80’s) in pH, Ca and Mg by 92-99 %. This stability in proportional inter- RC soil values seems not remarkably to have been affected by the equal nation-wide soil liming recommendations. Soil data have been collected by a private enterprise “Viljavuuspalvelu Oy” (since 2014 “Eurofins Viljavuuspalvelu Oy”) depending on the activity of the farmers. Additionally the number of Mg samples was lower than the number of “basic” samples until 1985, e.g. in 1966-70 the number of Ca samples was ca 400,000, but by Mg “only” ca 33,000” [8]. Obviously less biased sample series could show even higher associations, e.g. combined regression by provincial Si.gw and their capital Temp (4) can explain soil pH variation more than 90 %. This proportional inter-RC stability in the soil factors could explain the stability in proportional CHD mortality between provinces [9]. Association of groundwater with local food could (at least have been) promoted by long-root plants like alfalfa and red clover, which could benefit gw better than short-root plants. Evotranspiration (E0) [10] on Finnish croplands varies with the effective temperature sum (ETS) [11]

Figure 1: Combined regression by pH.(60’s) and pH.(70’s) explained pH.(80’s) by 96.8 % (p < 0.001).

Figure 2: Combined regression by Ca.(60’s) and Ca.(70’s) explained Ca.(80’s) by 99.3 % (p < 0.001).

Figure 3: Combined regression by Mg.(60’s) and Mg.(70’s) explained Mg.(80’s) by 92.3 % (p < 0.001).

Figure 4: Combined regression by Temp and Si explained pH.(80’s) by 86.5 % (p < 0.001). Computation gave equation: pH [Temp;Si (mg/L)] = 6.02 + 0.16*Temp - 0.11*Si (mg/L).

Figure 5: Combined regression by Temp and pH.(80’s) explained Si by 77.5 % (p < 0.001): Computation gave equation: Si (mg/L) = 38.5 + 1.14*Temp - 6.12* pH.

E0 = -100 + 0.388 *ETS (mm year-1), i.e. ca 2.5 - 4 million l/ha.

If one million liters of this came from gw, plants could get annually on the average 15 kg Ca, 3.8 kg Mg/ha and 6.5 kg Si/ha [6]. These values respond ca 1/4 of Ca and 1/3 of Mg total supply by fertilizers at the first half of the 1950’s [12] and possibly several folds the Si given in fertilizers, because in the 1970’s Si/Mg ratio in Finnish food was 0.008 [13]. Losses of Ca and Mg have been replaced, maybe now is the time to correct the Si losses [14-16].

Conclusion

Groundwater silicon is associated with the soil matrix factor (sources of groundwater silicon/silicon colloids?), which seems with temperature to explain inter-areal pH variation and obviously is associated with relative local stability of cropland Ca and Mg (and soil fertility). Maybe now is the time to increase Si trials in agriculture.

References

  1. pH 1961-2000: “http://www.viljavuuspalvelu.fi/index.php?id=107”, “Taulukko_4.doc “.
  2. Ca 1961-2000: ”http://www.viljavuuspalvelu.fi/index.php?id=107 -> Taulukko 5”.
  3. Mg 1961-2000”http://www.viljavuuspalvelu.fi/index.php?id=107 -> Taulukko 8”.Data 1,2,3 are now available from Eurofins Viljavuuspalvelu Oy: viljavuuspalvelu@eurofins.fi
  4. Toysa T (2016) Soil Weathering, Silicon and CHD in Finland. J J Agriculture 2(1): 8.
  5. Agricultural Advisory Centre (1988) Official Statistics of Finland: Farm Register [printed product]. Agriculture and forestry 1990:1992.
  6. Lahermo P, Tarvainen T, Hatakka T, Backman B, Juntunen R, et al. (2002) Tuhat kaivoa - Suomen kaivovesien fysikaalis-kemiallinen laatu vuonna 1999.
  7. FMI: Mean annual temperature.
  8. Viljavuuspalvelu Oy Helsinki (1972) Kurki Martti Suomen peltojen viljavuudesta II. Yhteiskirjapaino Oy.
  9. Toysa T (2015) Agro-Geology and CHD in Finland. J J Agriculture 1(2): 6.
  10. Solantie RK, Joukola MPJ Evotranspiration 1961-90 in Finland as function of meteorological and land-type factors. Boreal Environment Research 6: 261-273.
  11. Lahermo P, Tarvainen T, Hatakka T, Backman B, Juntunen R, et al. (2002) Tuhat kaivoa - Suomen kaivovesien fysikaalis-kemiallinen laatu vuonna 1999. Geologian Tutkimuskeskus. Tutkimusraportti 155. Geological Survey of Finland.
  12. Toysa Timo (2016) Compliance of Finnish Male CHD and Total Mortality with Soil Fertilization in 1957-1990. J J Agriculture 2(1): 13.
  13. Varo P, Koivistoinen P (1980) Chapter XII, General Discussion and Nutritional Evaluation: 165-171. In Koivistoinen P (Eds.), Mineral Element Composition of Finnish Foods: N, K, Ca, Mg, P, S, Fe, Cu, Mn, Zn, Mo, Co, Ni, Cr, F, Se, Si, Rb, Al, B, Br, Hg, As, Cd, Pb and Ash. Acta Agriculture Scandinavia Supplemental 22. Stockholm 1980. Average available daily supplies of mineral elements from Finnish foods, pp. 166
  14. Epstein, E Silicon (1999) Annual Review of Plant Physiology and Plant Molecular Biology 50: 641-664.
  15. Hensel J (1894) Bread from Stones: A New and Rational System of Land Fertilization and Physical Regeneration.
  16. Ma JF, Takahashi E (2002) Soil, Fertilizer, and Plant Silicon Research in Japan. (1st edn.) Survey on Si fertility, pp. 281.