THE ELECTROCHEMICAL OF NATURAL CHARACTERISTICS REDOX CELLS M. Whitfield’ CSIRO Division of Fisheries and Oceanography, Cronulla, N.S.W. 2230, Australia P.O. Box 21, The discharge characteristics of a range of natural rcdox cells have been monitorccl. The equilibrium cxchangc current densities ( i,,) have been calculated and compared with the The results indicate that instrumental current drains imposed by modern clectromctcrs. loading should bc negligible, but the small values of i,, observed may result in the slow This effect may not bc so serious in reduced scdiattainment of a steady-state potential. ments where the Eh is closely correlated with sulfide activity. In other cases some of the irrcgularitics in electrode behavior may be removed by discharging the ccl1 in situ and mcnsrning its rcchargc characteristics. INTRODUCTION Although Eh mcasurcmcnts2 have been used for many years to charactcrizc marine and freshwater sediments (cl;. see Mortimer 1941, 1942; Zo,Bell 1946) it is only recently that the mechanistic limitations of thcsc mcasurcmcnts have been trcatcd in detail (Stumm 1965). Morris and Stumm ( 1967, p, 279) stated that since natural waters are generally in a dynamic rather than an eauilibrium condition. even the concept of a single oxidation-reduction potential characteristic of the aqueous environment cannot bc maintained. At best. measurements can reveal an Eli value appli: cable to a particular system or systems in partial chemical equilibrium and then only if the systems are electrochemically reversible at the electrode surface at a rate that is rapid compared with the electron drain or supply by way of the measuring elcc,trode. In a rcccnt paper (Whitficld I969) I attcmptcd to show that the ope~ntional use of Eh as a parameter to charactcrizc the estuarine cnvironmcnt is not dcpcndcnt on the interpretation of this parameter as a true oxidation-reduction -potential and that useful and self-consistent results can bc obtained if suitable cxpcrimcntal prccauL Present address: Marinc Biological Association, The Laboratory, Citadel I-Iill, Plymouth PLl 2PB, England. 2 Ela is the potential, expressed on the standard hydrogen scale, generated at a bright platinum electrode immersecl in the sample. LIMNOLOGY AND OCEANOGRAPIIY Cons arc taken. This empirical approach to the use of Eh measurements rests hcavily on the assumption that the rate of clcctron exchange at the clcctrodc surface is sufficiently large to maintain a stcadystate potential in the face of the current drain or load imposed by the measuring instrument (see the last section of the quotation from Morris and Stumm). If this is not so then drifting and unsteady potentials will bc observed even if the environment is not disturbed at a11 by the insertion of the probe. The equilibrium cxchangc current dcnsity ( if) ) gives a measure of the rate of the clcctron cxchangc reaction; its significance in the interpretation of Eh mcasurcments was discussed by Stumm ( 1965) and by Morris and Stumm (1967). They concluded that a threshold value of about 1O-7 A cin2 for i0 is the minimum that can bc cxpectcd to sustain a steady-state potential. Further, they indicated that, of the rcdox sysems significant in natural waters, only the Fc2+-Fe3-k and Mn” t-Mn’-‘- couples arc capable oE sustaining cxchangc currents of this order. Thcsc couples would only be significant in cnrichcd waters where the dissolved iron or mangancsc contents are grcatcr than lo-‘) M. These conclusions h aVC been given some cxpcrimcntal support by the work of Bohn ( 196s) and of Peshchcvitsky ct al. ( 1967). This paper dcscribcs expcrimcnts de- 383 MAY 1972, V. 17(3) 384 M. WIIITPIELD signed to determine equilibrium exchange current densities in a variety of natural redox cells. The same experiments also permit quantitative assessment of the interesting possibility of using such cells as energy producers. For example, the “builtin” potential difference (up to 660 mV) across the sediment-water interface could be used to generate power by immersing one array of inert electrodes in the mud and exposing a second array to the overlying water. Since the electrodes are not consumed in the cell reaction, such an array could function indefinitely provided that the system was ahowed to (and was able to) recharge periodically by switching off the load. The feasibility of such a system can be assessed by observing the behavior of such cells under load. Here again the exchange current density is critical. METHODS The investigations must cover a wide range of conditions since Eh measurements have been used to characterize the from whole spectrum of environments well-aerated surface waters to stagnant reduced sediments (e.g. Baas Bccking et al. 1960; Krumbein and Garrels 1952). In addition the nature of the sediments will vary from location to location and, in view of the complexity of natural redox systems, this may have a crucial influence on the reproducibility of Eh measurements. The simplest way to span this wide range is to consider the characteristics of natural redox cells of the form Inert metal anode 1 reduced layer oxidized 1ayer 1 inert metal cathode cell I, rather than to use the conventional Eh measurement, Reference electrode 1 reference solution sample solution [ inert ccl1 for metal cell II. When cell I is allowed to discharge through an external load (e.g. a standard resistance) the flow of current through the cell, and hence through the external circuit, will be opposed by activation barricrs at the surfaces of the inert electrodes. To enable the electrons to surmount these barriers, a potential is established within the cell in opposition to the equilibrium (or steady state) potential; this is known as the current-produced overpotential (q). Once a new steady state has been achieved to balance the imposed current drain the net currents that flow through the anode and through the cathode must be equal. Naturally, the magnitude of the steadystate current (I) and the overpotential (r]) wiI1 be controhed by the highest activation barrier to be overcome; i.e. the equilibrium exchange current density (io) measured with cell I should represent the lowest value that might be expected in the range of environments spanned by the oxidized and reduced layers. Thus cell I can be used to give a limiting value for the exchange current (at least in terms of the order of magnitude) that might be experienced over a wide range of environmental conditions. If water in equilibrium with the atmosphere is always used in the oxidized layer then variations in the nature of the reduced layer can be used to assess the effects of differing sediment compositions. The loading characteristics of cell I will also illustrate directly the energyproducing potentialities of natural redox systems. The cells studied represent the systems air-saturated water-anoxic water ( cells A to C, Table 1) and air-saturated waterreduced sediments ( cells D and E ) . Cells A to C were designed to contain fairly high concentrations of degraded organic material (the water in the vicinity of the clcctrodcs was discolored by material released from the putrefying substrate), and cells D and E were representative examples of the usual field situation. Cells A to C were established in l-liter measuring cylinders by laying the ingredients of the solid substrate in the base of the cylinder to a depth of about 24 cm. The inert metal electrodes were then placed in position: one set 5 cm from the CIIARACTERISTICS TABLE 1. OF Summary NATURAL REDOX 385 CELLS of redox cells studied Inert electrode Cell type A B C D E Reduced substrate Oxidized substrate* Freshwater Freshwater Freshwater Seawater Seawater * In equilibrium with Seawater enriched above reduced mud with minced meat Reduced mud Mud at roots of Zostera Geometric surfnce mm (cm2) TYP bed Platinum mesh Platinum sheet Gold sheet Platinum mesh Platinum mesh cathode Platinum sheet anode 13.0 2.3 6.0 13.0 13.0 6.0 the air. lip of the cylinder and the other set 1 cm above the sediment surface. Freshwater ( 300 ml) was then added carefully so as not to disturb the sediment layer. Afterwards, 700 ml of fresh seawater at the same temperature were added slowly via a PVC tube with its tip just above the sediment-water interface. In this way, a sharp stratification was established, enabling stagnant conditions to build up fairly rapidly in the water layer immediately above the sediment surface. These cells have a useful life of 7-10 days before the stratification is broken by the stirring action of gas bubbles released from the dccaying substrate, Similar cells have been prepared by Skopintsev et al. ( 1967)) who have shown that the cells are capable of recovering quite rapidly from an intermittent load. Cell D was prepared by placing about 500 ml of a silty, reduced sediment in the bottom of a e-liter beaker and adding 1.5 liters of fresh seawater. One set of electrodes was immersed to a depth of 2-3 cm in the mud and the other to a similar depth in the overlying seawater. The sediment samples used in cells A-D were taken from the area of reduced, silty sediment in Gunnamatta Bay, Sydney (Whitfield 1969 ) , Cell E was established in situ by inserting a cylindrical platinum sheet electrode to a depth of 10 cm in the silt underlying a Zostera bed. The platinum mesh cathode was suspended from a float in the overlying water. The mesh clcctrodcs used in all cells were cleaned by cathodic elcc- trolysis in 0.001 M sulfuric acid for 15 min followed by rinsing in distilled water. The sheet electrodes were rubbed with a fine emery cloth before cathodic cleaning. The cells were left overnight to attain a stable potential (drift less than 5 mV/hr) and to equilibrate to room temperature (20 +- 2C). The resistance box (R, Fig. 1) was then adjusted to the desired value and the cell allowed to discharge through the load by depressing the switch ( S ). The discharge curve was recorded continuously on the potcntiomctric recorder (sensitivity, 500 mV full-scale deflection; recording speed 50 mm/min) and potentials were read off at frequent intervals from the voltmeter and written on the chart. After a stable potential had been attained (drift less than 0.1 mV/min) the load was disconnected and the recharging charactcristics of the ccl1 were measured in the same way. A stable potential was normally attained within 2-4 min of switching in the load and the ccl1 potential would spring back to its initial value when a similar time had elapsed after the load had been disconnected. RESULTS AND DISCUSSION Most measurements were made on cells of type A (Table 1) because they were considered to represent a worst case for the reproducibility of Eh measurements, The rcduccd phase is very rich in organic material and the clectrodc potential more likely to be disturbed by water movements in the vicinity of the electrode than 386 0.8 (a) Recorder -i> I E. 0.4 u .!5 +I> A 4pd II 2.: 0 A’2 I II II , , , , , I (b) Voltmeter 1.6 -i > E M .% +I> 0.8 FIG. 1. Circuit for measuring loading characteristics of natural redox cells. For cells A to D ( Table 1) ( b ) was a Dynamco DM2022 digital voltmctcr. For cell I3 (a) was omitted and (b) was a Keithlcy model 610 battery-opcratcd electrometer. is the case for interstitial water in the scdimcnts. The charge and discharge curves for all the cells fit an equation of the form v = t/+1 + ht), (1) where V is the cell potential at time t and a and b arc constants. Response curves of platinum electrodes immcdiatcly after insertion into a sample oE reduced mud appear to follow a similar relationship (e.g. Whitfield 1969). However, the behavior of thcsc curves becomes erratic after 10 or 15 min, probably bccausc of enhanced bacterial action in the small sample container. The steady-state potential approached dur- 100 t (sets) Fro. 2. Charging and discharging curves for cell A plotted according to equation (4). A. Charging curves for experiments A8C ( O), A9C and AlOC ( 0 ). B. Discharging curves. (A> Numbers on the graphs correspond with the data points for cell A listed in Table 2. ing charge or discharge ( V, ) and the half time of the process (tlh, time when V = V, /2) can be obtained from the relationships V, = 1/b (2) t1/$= 1cc/h 1. (3) Equation ( 1) has the same form as the equation used to describe the response of an ion-sclectivc electrode to a sudden step in the concentration of the selcctcd ion ( Mullcr 1969)) and it also bears a formal rcscmblancc to the Langmuir adsorption isotherm and the Michaelis-Mentcn cquation for enzyme activation kinetics. CIIARACTERlSTICS TABLE (1) Code A 1D 2D 3D 4D 5D 6T> 7D 8D 9D 1011 11D 12D 13D 14D 8C (;J ‘v3’ (9 x 10-q n (1nV) 101 102 105 110 125 150 1,300 53 33 9 75 5 20 53 Open cimii t 9c 1OC 11c 12c 13c G”’ m (mV) 2. (5) 1‘h (see) OF NATURAL Summary* of data from (7) (0) SE x 102 REDOX (nk) (8) 387 CELLS cells (10) i (nA m-2) (y) &, (PA) 87.1 88.0 87.1 88.0 84.8 76.3 17.0 169.6 179.7 331.0 88.0 385.5 239.0 167.3 - (CLW) 0.13 0.13 0.14 0.14 0.14 0.15 0.058 0.24 0.18 0.17 0.098 0.13 0.19 0.25 - 303 291 301 300 300 310 314 317 293 300 300 300 295 317 113 114 116 119 125 138 149 263 111 77 39 86 25 62 115 289 2.0 2.5 3.0 2.5 2.5 2.5 1.0 2.5 2.5 2.5 2.5 3.0 2.0 3.0 7.5 0.64 0.21 0.58 0.25 0.45 0.90 0.72 0.16 0.66 7.52 0.70 1.16 0.97 2.03 1.02 174 172 169 163 150 139 25 177 211 249 202 263 226 173 - 39.5 40.5 41.3 43.3 47.8 51.7 91.3 38.5 26.7 13.5 29.8 8.7 21.5 39.9 - 1.13 1.14 1.13 1.14 1.10 0.99 0.22 2.20 2.33 4.28 1.14 5.00 3.10 2.17 - 78 38 86 24 62 287 296 286 276 282 9.0 10.0 8.5 9.0 8.0 1.04 0.79 1.25 2.24 1.52 - - - - - 399 337 327 280 232 253 - 13.0 26.8 29.2 9.7 17.2 9.3 - 1.67 2.30 2.55 0.33 0.52 0.54 - 248 338 378 0.10 0.28 0.34 1D 2D 3D 41) 511 6D 1C 2c 3c 36 53 53 99 93 50 Open circni t 587 626 664 310 280 280 66 122 135 60 122 135 30 48 27 428 459 45s 9.0 8.5 8.5 3.5 2.0 3.0 19.0 12.0 9.5 C 1D 2D 3D 4D 10,000 8,311 4,911 1,411 322 220 200 161 221 169 136 69 13.5 3.5 2.5 4.5 8.03 1.08 2.16 7.49 101 51 64 92 68.6 76.7 68.0 42.8 2.2 2.0 2.8 4.9 D ID 211 3D 4D 5D 50 93 9 99 1 462 436 444 440 462 156 209 55 209 8 6.0 4.5 4.5 5.0 - 3.25 1.93 4.82 2.58 - 306 227 389 231 454 33.8 48.0 12.7 47.5 1.7 3.12 2.25 6.12 2.11 8.0 242 174.5 474 163.5 621 0.49 0.47 0.34 0.44 0.064 E 1D 2D 3D 111 61 11 165 165 165 110 85 26 - - 55 80 139 66.8 51.5 15.8 0.99 1.39 2.69 104.2 146.2 248.4 0.11 0.12 0.061 T3 51.2 23.5 21.7 19.7 14.7 11.3 17.0 13.0 34.7 E 80 x x x x lo-? lo-? lo-” lo-? 3.56 3.24 4.53 7.94 0.010 0.025 0.015 4.9 3.4 3.8 3.4 x x x x lo-” lo-” lo-’ lo-:’ * All symbols usccl in columns ( 2) to ( 11) are explained in the text. Column l--Suffix D refers to n discharging cell ancl suffix C to R charging cell. Prefix refers to cell type (Table 1). Column 3-V(, values based on leveling off of recorder trace. Columns 7 and S-For cells A and B, V, vnlucs nr.e estimated from the appropriate discharge curves and not from column 3. Cells A and C were 4 days old. Cells Bl to n3 were 1 clay old and cells R4 to BG were 3 clays old. Equation ( 1) was cxpresscd in the form (t/V)=a+ht, (4) and the data wcsc fitted to this equation by the method of lcast squares (Table 2 colu~l~s 4-6). The fit was exccllcnt for cells A, C, and D and the values obtained for V, on discharging agreed within a few millivolts with the values cstimatcd from the lcvcling-off of the rccordcr trncc nftcr 388 M. WHITFIELD “Tafel” or “high field” plot for the FIG. 3. discharge of all cells ( equation 7 ) . A- 0 ; B0; C-A; D-V; E-V. Data points representing the first discharge of each cell are marked with a horizontal bar. 200 set of discharge. The agreement was not so good with cell B but the values of V, obtained were within 5 mV of the values estimated from the chart. Some of the raw data for cell A are plotted in Fig. 2; the discharge curves fan out from a common origin whereas the data for recharging curves fall closely about a single straight line. These data also illustrate well the closeness of fit to equation ( 1) as specified in Table 2 ( column 6). The internal consistency of the half times for each cell suggests that the same process is being monitored during each discharge. The half times for cells A and B are the same (about 2.5 set) after 3 days running whereas the value for fresh cells is much greater (about 8.5 set) . The half time for recharging is consistently longer than that for the discharge process in cells A and B; the equilibrium potential predicted from the straight-line fit is consistently lower than that actually observed after about 5 min recharging time. This suggests that two separate processes may be responsible for fixing the cell potential; one associated with an electron exchange reaction, being monitored by the charge and discharge curves and the other associated with the presence of adsorbed species on the electrode surface. This may be coupled with the observation that the first discharge of any of the cells after an overnight charge gives an anomalously large overpotential (see Fig. 3). The asymmetry of the half times is consistent with the suggestion of Stumm (1965) and Bohn (1968) that the platinum electrode records a mixed potential in natural media. From the data obtained from equation ( 1) it is possible to calculate the currentproduced overpotential (7 = V, - V,), the voltage efficiency of the cell ( E = 100 *V, /VO), the steady-state current (I = V,/R) , the steady-state current density (i = I/electrode area), and the wattage output in the steady state (W = Vw2/R = V,.?‘). These data arc listed in Table 2 (columns 7-11). For an energy-producing cell the overpotential (q) may be related to the current density (i) by the Butler-Volmer equation which in its simplest form can be written as i = i,[e(l-B)h -e-L%], where p is a parameter dependent electrode reactions and k = nF/RT = 16.7nV-2 (5) on the at 25C, (6) where n is the stoichiometric number of electrons associated with the overall cell reaction and the other terms have their usual significance. If, under load, the system is pulled well away from equilibrium then q is large and the second term on the right-hand side of equation (5) tends to zero so that i = ioe(l-8)We (7) Equation (7) is known as the “high field’ This equation has been approximation. CHARACTERISTICS OF shown to hold for values of 7 greater than 120 mV for a single electron process (Bockris and Reddy 1970) and the threshold potential is lower for multielectron processes, Therefore a plot of 7 vs. log i for my data should give a straight line and the intercept on the current axis will give the equilibrium exchange current density ( i0 ) for the overall cell reaction. The data (Fig. 3) confirm that the high field approximation is obeyed within the limits of experimental error. Such an agreement would not be observed if thcrc were gross inhomogcneities in the electrode surface or if the properties of the electrode surface changed appreciably during the course of the experiments (Ives and Janz 1961). All the cells give cquilibrium current densities below the threshold value of 10m7A cm-2 suggested by Stumm (1965) and by Morris and Stumm (1967). The cell using gold electrodes is particularly poor with an i0 value of 10-O A cm-2. This explains why gold electrodes have behaved poorly in natural media (Barnes and Back 1964; Whitfield 1969) and is consistent with the relative behavior of platinum and gold in the hydrogen elcctrode (Bockris and Rcddy 1970). In the cells using platinum electrodes the i0 values for the cylinder cell ( cells A and B ) and the mud cell ( cells D and E ) are self-consistent despite the different surface areas and electrode types involved (Table 1). It may be argued that the results reprcsent a concentration rather than an activation overpotential; in other words, the energy barrier controlling electron transfer is caused by slow diffusion of the reactants to the electrode surface rather than by a sluggish reaction there. If this were true then erratic potentials would bc obtained unless a consistent degree of stirring or stagnation were maintained while the mcasurements were being made. This would make the operational use of Eh in field studies unrealistic. For a transport controlled reaction, the concentration ovcrpotential (qo) and the current density (i) arc related by an equation of the form NATURAL REDOX 389 CELLS I 0.1 -“I I 0.2 (Volts) FIG. 4. Plot of current density (i) vs. overpotential ( 7 ) for cell A indicating that r is an activation rather than a concentration overpotential (see equation 8). i = i,(l-ea’lc) (8) (e.g. see Bockris and Reddy 1970). If i is plotted against Q, a limiting current density is approached as qC becomes more negative. A plot of i vs. 7 for cell A shows no sign of a limiting current density and is characteristic of an activation overpotential ( Fig. 4). A comparison of the curves in Fig. 3 indicates that this is true for all the cells studied. The potential measured here is therefore not diffusion controlled. This might bc expected because of the extremely low current fluxes generated in the cells. To assess the errors involved in poten- 390 M. WIIITFIELD tiomctric mcasurcmcnts we can consider equation ( 6) when the system is close to equilibrium ( 7 is very small) ; i is then rclatcd to ‘1 by the “low field” approximation, i=i()kTj. (9) If we consider a small current Ai passing through the system this will gcncratc an ovcrpotcntial Aq so that, Ai = i,,karj. (10) If WC need to know the ccl1 potential to the ncarcst 10 mV (the limit of rcproducibility of field mcasurcmcnts ) then the maximum current to be drawn by the measuring instrument is about 1O-9 A for each square ccntimctcr of clcctrodc surf act. This may bc compared with the offset current of a typical pH mctcr (lo-IL A) and that of the Kcithlcy 610C electrometer used in earlier measurcmcnts ( 10-l” A: Whitfield 1969). High input impedanccmeasuring devices have been used successfully to measure the potentials of metal oxide elcctrodcs having cxchangc current densities of the order of 1O-7 A cm-2 (Ives and Janz 1961). Thcrcfore thcrc is no reason, from the point of view of instrumental loading, why fairly rcproduciblc potential measurements should not bc made. However, Eh measurements should not bc made with a manually balanced potentiometer or with a sclf-balancing potcntiomctric recorder. From the point of view of polarization, the cells must bc trcatcd as high impedance sources ( Barnes and Back 1964). With such low current densities the steady-state potential may bc attained only slowly. This is often the case in oxidizing environments where equilibration times as long as 8 hr have been recorded (Barnes and Back 1964). The i. values rcportcd hcrc represent the lowest values to bc cxpccted in the rcdox range spanned by cell I and more favorable conditions might prevail in a reducing cnvironmcnt. The relationship between sulfide activity and Eh in reducing marinc and cstuarinc scdimcnts (Berner 1963; Kryukov et al. 1962; Skopintsev ct al. 1967; Whitficld 1969) indi- FIG. 5. Plot of current density (i) vs. voltage efficiency (E) for cells A ( 0 ), C (A), D (O), and E (v). V a1ucs for the ordinate of cell C have been multiplied by 100 to bring them on scale. catcs that a fairly simple reaction controls the potential of the platinum electrode, and steady-state potentials arc achieved fairly rapidly if cart is taken to prcvcnt undue disturbance of the sample. Further studies using cell II with the platinum elcctrodc immersed in a reducing cnvironmcnt would help to dcfinc more rigorousIy the limits of reproducibility of Eh mcasurcmcnts under these conditions. Where slow attainment of the steady state is a problem a discharge-charge procedure may bc used together with equations (1) and (2) to estimate the final potcntia1. Such a proccdurc has been suggcstcd by Mullcr (1969) for use with high resistance mcmbranc clcctrodes where similar problems arc cncountercd. A reproducibility of +25 mV is quite adequate for the operational USC of Eh values since useful pictures can bc built up by rounding off the Eh values to the nearest 50 mV CIIARACTIZRlSTICS OF FiATURAL REDOX 391 CELLS ‘0 t (mins) i (pAcm-2) FIG. 0. Plot of power output (W) vs. current density (i) f or cells A (01, C (A>, D (V), and aband E (v). V a1ues for the ordinate scissa of cell C have been multiplied by 100 and 50 respectively to bring them on scale. and drawing contours at lOO-mV intervals ( Whitfield 1969) . As might be expected from Fig. 3 the cells studied here do not rate very highly as power sources, Howcvcr, a brief look at their characteristics will help to confirm the internal consistency of the data prcscntcd here. Data for cell B will be omitted since the energy-producing properties of the cylinder cell vary considerably with age ( Table 2). Since the data for cell B were taken at different times in the cell lift no coherent picture can bc cstablishcd, although measurements B4D to B6D agree fairly well with those for cell A. The voltage efficiency of all cells incrcascs as the current density decreases ( Fig. 5) and therefore the output wattage passes through a maximum at some intcr- FIG. 7. Behavior of ccl1 A when a prolonged discharge. subjected to mediate current density (Fig. 6). This pattern of behavior is consistent with that obscrvcd with other energy-producing cells and the shape of the curves in Fig. 5 supports the assumption (used in the dcrivation of equation 5) that ohmic polarization within the cell is ncgligiblc. The current density and output power scales for the gold elcctrodc (cell C) have been cxpandcd considerably. The maximum power available from cell D is 0.48 ,uW at 300 n,A cm-2. When one of the cells was discharged for a prolonged period ( Fig. 7) the hyperbolic decay curve was followed for about 80 min and the potential then fell to a low value (20 mV in this cast) which was maintained at least for a furthcr 4 hr. Consequently some switching dcvicc would bc necdcd cvcn to maintain the peak output of 0.5 pW. A few such cells in series might bc able to cnergizc an electronic wristwatch! 392 M. WHITFIELD CONCLUSIONS By discharging a natural redox cell through an external load it is possible to obtain an estimate of the equilibrium exchange current density ( iO) accompanying the cell reaction. The i0 value is a measure of the rate of the overall cell reaction at the electrodes and it controls the polarizability of the cell, i.e. the magnitude of the overpotential ( 7) produced by the passage of current. Ideally potentiometric measurements should be made with a nonpolarizable cell so that small currents generated by the measuring instrument will not disturb the cell potential. The present measurements indicate that i0 is small ( <O.l ,X-LAcm-2) in the cells studied and that the cell potential is probably a mixed potential resulting from a series of irreversible reactions. Nonetheless, the cells behave reproducibly and their behavior can be described by relatively simple elcctrochemical equations. In addition, the i0 values observed for cells with a mud base were large compared with the input offset currents of modern electrometers. Taken together these observations indicate that reproducible Eh measurements can be obtained if the cell potential is controlled by a relatively simple series of reactions and a steady-state potential can be attained fairly rapidly. There is already evidence from widely separated regions that the potential of a bright platinum electrode is controlled by the couple So( rhombic) /HS-( aq. ) under reduced conditions (Berner 1963; Kryukov et al. 1962; Skopintsev et al. 1967; Whitfield 1969). It has also been suggested that under mildly oxidizing conditions the platinum electrode either reflects the irreversible oxygen potential (Cooper 1937) or that it behaves as a pH electrode of the second kind via the formation of Pt( OH)2 (Pcshchevitsky et al. 1967). To rationalize the wide spectrum of opinion over the utility of Eh measurements it would be valuable to consider these rcactions in greater detail. In addition, in situ measurements of i. using the approach described here could bc used to assess the feasibility of Eh measurements. The practice of discharging the cel1 through a load and plotting the recharge characteristics as a function of time might also help to reduce the effects of adsorbed organic material and poorly poised redox systems and enhance the reproducibility of Eh measurements. REFERENCES BAAS BECKING, L. G. M., I. R. KAPLAN, AND D. MOORE. 1960. Limits of the natural environment in terms of pH and oxidation-reduction potential. J. Geol. 68: 243-284. BARNES, I., AND W. BACK. 1964. Geochemistry of iron-rich ground water of southern Maryland. J. Geol. 72: 435-447. BERNER, R. A. 1963. Electrode studies of hydrogen sulfide in marine sediments. Geochim. Cosmochim. Acta 27: 563-575. BOCKFUS, J. O’M., AND A. K. N. REDDY. 1970. Modern electrochemistry, v. 2. McDonald. BOHN, M. L. 1968. Electromotive force of inert electrodes in soil suspensions. Soil Sci. Sot. Amer. Proc. 32: 211-215. COOPER, L. H. N. 1937. Oxidation-reduction potential in seawater. J. Mar. Biol. Ass. U.K. 22: 167-176. IVES, D. J. G., AND G. J. JANZ [EDs.] . 196,l. Reference electrodes. Academic. KRUMBEIN, W. C., AND R. M. CARRELS. 1952. Origin and classification of chemical sediments in terms of pH and oxidation-reduction potentials. J. Geol. 60: 1-33. KIIYUKOV, P. A., S. S. ZADODNOV, AND V. E. GOFIEMYKIN. 1962. Sulphide and carbonate equilibrium and the oxidation-reduction state of sulphur in the mineral regions of the Crimean mineral waters. Dokl. Akad. Nauk SSSR 142( 1). MORRIS, J. C., AND W. ST-. 1967. Redox equilibria and measurements of potentials in the aquatic environment, p. 270-285. Advan. Chem. Ser. 67. MORTIMER, C. H. 1941. The exchange of dissolved substances between mud and water in lakes. 1 and 2. J. Ecol. 29: 280-329. -. 1942. The exchange of dissolved substances between mud and water in lakes. 3. J. Ecol. 30: 147-201. MULLER, R. H. 1969. Commentary on new directions in ion-selective electrodes. Anal. Chem. 41: 113A-116A. PESEICHEVITSKY, B. E., N. M. NIKOLAE~A, AND B. A. VOROTNIKOV. 1967. The limits of application of smooth platinum electrodes in measuring Eh of natural waters. Geol. Geofiz. 1967( 9) : 32-40. CHARACTERISTICS OF SKOPINTSEV, B. A., N. N. ROMENSKAYA, AND E. V. Smov. 1987. New determinations of the oxidation-reduction potential in Black Sea water. Oceanology (USSR) 6 : 653-659. STUMM, W. 1965. Redox potential as an environmental parameter. Conceptual significance and operational limitation, p. 283-308. In 0. Jaag [ea.], Advances in water pollu- NATURAL REDOX CELLS 393 tion research, v. 1. Proc. Int. Water Pollut. Res. Conf., 2nd, Tokyo. Pcrgamon. WHITFIELD, M. 1969. Eh as an operational parameter in estuarine studies. Limnol. Oceanogr. 14: 547-558. ZOBELL, C. E. 1946. Studies on redox potential of marine sediments. Bull. Amer. Ass. Pctrol. Gcol. 30: 477-513.
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