Table 2 O2 consumption and DIC and TA production during sequential aerobic respiration, sulfate reduction and carbonate mineral dissolution in bottom waters45, 83
From: Redox reactions and weak buffering capacity lead to acidification in the Chesapeake Bay
Redox | Δ[O2] ( μmol kg−1) | ΔDIC ( μmol kg−1) | ΔTA ( μmol kg−1) | ΔTA/ΔDIC | pH | Ωarag |
|---|---|---|---|---|---|---|
AR | (CH2O)106(NH3)16(H3PO4) + 106O2 ↔ 106CO2 + 16HNO3 + H3PO4 + 122H2O | −(16+1)/106 = −0.16 | ||||
0 (100%) | 0 | 0 | 8.055 | 1.56 | ||
−58 (75%) | +45 | −7.2 | 7.859 | 1.05 | ||
−117(50%) | +90 | −14.4 | 7.629 | 0.65 | ||
−174(25%) | +134 | −21.5 | 7.421 | 0.40 | ||
−231.7(0%) | +178.0 | −28.5 | 7.237 | 0.26 | ||
SR | (CH2O)106(NH3)16(H3PO4) + 53SO4 2− → 106HCO3 − + 53H2S + 16NH3 + H3PO4 | (106+16−1)/106 = 1.142 | ||||
0 | +70.0 | +80.6 | 7.199 | 0.25 | ||
CD | CaCO3 + CO2 + H2O → Ca2+ + 2HCO3 − | 2/1 | ||||
0 | +57.6 | +115.3 | 7.368 | 0.38 | ||
Total | −231.7 | +305.6 | +167.3 | |||