Table 2.
Lake | CH4,av (µM) | Asurf (km2) | dSML (m) | RAV (m−1) | Prevailing biological process | RCH4 | NOMC (%) |
---|---|---|---|---|---|---|---|
Beauchene | 0.036 | 17 | 5 | 0.0099 | Production | 1.24 | 19 |
Champlain | 0.089 | 1269 | 10 | 0.0011 | Oxidation | 0.92 | −9 |
Camichagama | 0.025 | 26 | 7 | 0.0081 | Production | 1.21 | 17 |
Nominingue | 0.067 | 22 | 5 | 0.0087 | Production | 1.22 | 18 |
Ontario | 0.032 | 19,009 | 12 | 0.0003 | Production | 1.22 | 18 |
Simard | 0.040 | 170 | 10 | 0.0031 | Production | 1.41 | 29 |
St.-Jean | 0.009 | 1065 | 5 | 0.0012 | — | — | — |
The relative decrease/increase due to oxidation/production in the SML is given by RCH4 − 1. The contribution of net oxic production to diffusive CH4 emissions is NOMC = (RCH4 − 1)/RCH4. All data except for RAV and NOMC are from DelSontro et al.7. Results on all lakes and additional information are provided in Supplementary Table 5 (Supplementary Note 4.1).
CH4,av average CH4 concentration in the SML, Asurf surface area, dSML depth of the surface mixed layer SML, RAV Ased/VSLM assuming a sediment slope of 5°, Ased sediment area in the SML, VSLM volume of the SML, RCH4 ratio of total emissions to total littoral flux (Supplementary Note 4).