Limits of the Natural Environment in Terms of pH and Oxidation-Reduction Potentials

1. The electron and the proton content (measured as electrode potential [Eh] and pH) of an environment characterize this environment in many ways. In this paper the electrode potential and the pH are used as empirical parameters rather than as electrochemical data capable of thermodynamic interpretation. From published and unpublished work by the authors and from the literature, more than 6,200 pairs of characteristics were gathered, covering most types of the aqueous environment as well as the potential milieu of the chief actors in these environments: algae and bacteria. 2. It appears that the Eh-pH limits of biological systems and of the naturally occurring aqueous environment almost coincide. This would indicate that there are few, if any, sterile terrestrial environments caused by limiting Eh-pH characteristics. 3. As it seems unlikely that environments will be found outside the limits outlined in this paper, physico-chemical speculations on the sedimentary environment should be limited by this outline. Substances which do not occur (sulfuric acid, sulfide ion) should not be used in the electrochemical characterization of the environment. 4. The biogenic master reaction in the environment, changing one or both characteristics (Eh-pH), is reductive photosynthesis by algae and by colored bacteria. A photosynthetic mass may raise the pH of a water to 9.4; and in the absence of bivalent cations, to 12.6. 5. The intensity of sulfate reduction depends upon the sulfate content of the water and on the available hydrogen, in both organic and inorganic form. The iron concentration is also important, as iron is the principal acceptor of the $$H_{2}S$$ formed. The highly reactive, black iron Sulfides may be partly oxidized with the formation of the more stable pyrite and marcasite. The reduction of iron from ferric to ferrous state takes place even in surface soil. 6. Denitrification, another biologically important reduction, may be of lesser geochemical influence. 7. Oxidative reactions comprise, apart from nitrification, chiefly the oxidation of $$H_{2}S$$ and $$SH^{-}$$ to sulfur, thiosulfate, sulfite, hydrosulfite, sulfate, and hydrosulfate and the oxidation of ferrous and manganous compounds. In contrast with the reductions, these oxidations are only in part biological. The oxidation of pyrite may give rise to extremely low pH values. Heterotrophic oxidation (respiration) results in the conversion of organic matter into $$CO_{2}$$ and $$H_{2}O$$. 8. Acid formation in peat bogs is caused largely by cation exchange on plant cell walls, chiefly, but not exclusively, on Sphagnum. 9. In sediments the reaction between iron phosphate complexes and $$H_{2}S$$ may liberate the acid $$H_{2}PO_{4}^{-}$$ ion. 10. Certain environments are restricted, others cover almost the maximal area outlined in this paper. A progressive increase in the environmental range, arranged in a series, follows: rain water, mine water, peat bogs, sea water, rivers and lakes, marine sediments, and evaporites, while the geothermal environment shows the maximal area. 11. The potential milieu of the green bacteria is highly restricted. Less restricted is the environment of the iron bacteria, followed by sulfate-reducing bacteria, purple bacteria, and denitrifying bacteria. Thio-bacteria have a very wide potential milieu, and algae are found literally everywhere. 12. The Eh-pH characteristics are determined chiefly by photosynthesis, by respiration and by oxido-reductive changes in the iron and sulfur systems.

[1]  H. B. Stewart Sedimentary Reflections of Depositional Environment in San Miguel Lagoon, Baja California, Mexico , 1958 .

[2]  R. Garrels,et al.  Thermodynamic equilibria of vanadium in aqueous systems as applied to the interpretation of the Colorado Plateau ore deposits , 1958 .

[3]  D. Carroll Role of clay minerals in the transportation of iron , 1958 .

[4]  D. White THERMAL WATERS OF VOLCANIC ORIGIN , 1957 .

[5]  H. Skinner,et al.  Dolomite sedimentation in the south-east of South Australia , 1957 .

[6]  J. Postgate,et al.  Sodium chloride and the growth of Desulphovibrio desuplphuricans. , 1957, Journal of general microbiology.

[7]  K. Krauskopf Dissolution and precipitation of silica at low temperatures , 1956 .

[8]  W. L. Orr,et al.  Regeneration of nutrients in sediments of marine basins , 1955 .

[9]  D. G. Moore,et al.  Central Texas Coast Sedimentation: Characteristics of Sedimentary Environment, Recent History, and Diagenesis: PART 1 , 1955 .

[10]  F. Swain,et al.  STRATIGRAPHIC DISTRIBUTION OF LIPOID SUBSTANCES IN CEDAR CREEK BOG, MINNESOTA , 1954 .

[11]  R. Garrels Mineral species as functions of pH and oxidation-reduction potentials, with special reference to the zone of oxidation and secondary enrichment of sulphide ore deposits , 1954 .

[12]  Paul V. Smith Studies on Origin of Petroleum: Occurrence of Hydrocarbons in Recent Sediments , 1954 .

[13]  R. Garrels,et al.  Relation of pH and oxidation potential to sedimentary iron mineral formation , 1953 .

[14]  K. Emery,et al.  Early diagenesis of California Basin sediments in relation to origin of oil , 1952 .

[15]  M. Soule Oxidation-Reduction Potentials in Bacteriology and Biochemistry , 1951 .

[16]  K. Temple,et al.  AN IRON-OXIDIZING BACTERIUM FROM THE ACID DRAINAGE OF SOME BITUMINOUS COAL MINES , 1950, Journal of bacteriology.

[17]  J. Postgate Competitive Inhibition of Sulphate Reduction by Selenate , 1949, Nature.

[18]  E. Gorham Some chemical aspects of a peat profile , 1949 .

[19]  R. E. Oesper,et al.  Laboratory Manual of Spot Tests , 1947 .

[20]  R. Starkey,et al.  Anaerobic Corrosion of Iron in Soil , 1946 .

[21]  C. E. Zobell Studies on Redox Potential of Marine Sediments , 1946 .

[22]  Clifford H. Mortimer,et al.  THE EXCHANGE OF DISSOLVED SUBSTANCES BETWEEN MUD AND WATER IN LAKES, II , 1941 .

[23]  G. E. Hutchinson,et al.  The Oxidation-Reduction Potentials of Lake Waters and Their Ecological Significance. , 1939, Proceedings of the National Academy of Sciences of the United States of America.

[24]  L. Rettger,et al.  Bacterial Oxidation-Reduction Studies , 1938, Journal of bacteriology.

[25]  R. Misra Edaphic Factors in the Distribution of Aquatic Plants in the English Lakes , 1938 .

[26]  W. Pearsall The Soil Complex in Relation to Plant Communities: I. Oxidation-Reduction Potentials in Soils , 1938 .

[27]  S. G. Heintze The use of the Glass Electrode in Soil Reaction and Oxidation-Reduction Potential Measurements , 1934, The Journal of Agricultural Science.

[28]  E. Kindle A Comparative Study of Different Types of Thermal Stratification in Lakes and Their Influence on the Formation of Marl , 1929, The Journal of Geology.

[29]  C. S. McKee The Determination of Hydrogen Ions , 1928 .

[30]  T. Hoering The isotopic composition of the ammonia and the nitrate ion in rain , 1957 .

[31]  C. B. van Niel Natural selection in the microbial world. , 1955, Journal of general microbiology.

[32]  K. Str⊘m Land-Locked Waters and the Deposition of Black Muds , 1955 .

[33]  K. H. Schutte,et al.  The Significance of Large pH Fluctuations Observed in Some South African Vleis , 1954 .

[34]  G. Deacon The Oceans , 1945, Nature.

[35]  R. J. Allgeier,et al.  Oxidation-reduction potentials and pH of lake waters and of lake sediments , 1941 .

[36]  J. Spek Bijdrage tot de kennis van de zure gronden in het Nederlandsch alluvium , 1934 .

[37]  R. H.,et al.  Iron Bacteria , 1920, Nature.