Mi­crobes and Methane

by Roberto

The three green­house gases that con­tribute most to global warm­ing are car­bon diox­ide (CO2), methane (CH4), and ni­trous ox­ide (N2O). There is, of course, an ur­gent need to re­duce the emis­sions of all. How­ever, two facts point to methane emis­sion re­duc­tion as the most im­pact­ful in the near term. First, its half-life in the at­mos­phere (7−12 years) is much shorter than that of CO2, which can per­sist for hun­dreds of years. Sec­ond, be­cause of its in­her­ent phys­i­cal-chem­i­cal prop­er­ties, methane's global warm­ing po­ten­tial per unit mass is 80 times greater than that of CO2. Be­cause mi­crobes are in­volved in methane pro­duc­tion (methanogens) and con­sump­tion (methan­otrophs), mi­cro­bi­ol­ogy will un­doubt­edly play a huge role in methane emis­sion mit­i­ga­tion. I say, we need to know as much as pos­si­ble about mi­crobes and methane.

Fig. 1. The global methane bud­get for year 2017 based on top-down meth­ods for nat­ural sources and sinks (green), an­thro­pogenic sources (or­ange), and mixed nat­ural and an­thro­pogenic sources (hatched or­ange-green for 'bio­mass and bio­fuel burn­ing'). Source. Fron­tispiece: from the cover of AAM re­port. Source

If you're look­ing for a primer on mi­crobes and methane (as was I, re­cently) I di­rect you to a timely re­port from an Amer­i­can Acad­emy of Mi­cro­bi­ol­ogy (AAM) col­lo­quium on the sub­ject. It's ex­cel­lent read­ing as it con­tains a trea­sure trove of in­for­ma­tion along with an im­pres­sive list of ref­er­ences, for those who want to take a deeper dive into the sub­ject. What are the main sources of methane emis­sions? Large amounts of methane are re­leased from the fos­sil fuel in­dus­try and sadly, they mostly come from "su­per-emit­ter events," the re­sult of equip­ment fail­ures. But in con­trast to CO2 emis­sions, which come over­whelm­ingly from burn­ing fos­sil fu­els, agri­cul­ture and waste are the ma­jor sources of at­mos­pheric methane. The AAM re­port fo­cuses on four methane sources where the au­thors saw the great­est po­ten­tial for mit­i­ga­tion in the short term: en­teric fer­men­ta­tion in ru­mi­nants, an­i­mal wastes, rice pad­dies, and land­fills. For each of these, the re­port out­lines what is known about the mi­crobes and mi­cro­bial ac­tiv­i­ties and which knowl­edge gaps need to be ad­dressed. These are fol­lowed by de­scrip­tions of pos­si­ble mit­i­ga­tion strate­gies. It is en­cour­ag­ing to know that, even with our still in­com­plete knowl­edge of the mi­cro­bial ac­tiv­i­ties in­volved, ex­perts fore­see ways in which mi­crobes could be used to re­duce methane emis­sions rea­son­ably quickly. For any mi­cro­bi­ol­o­gist wish­ing to em­bark in cli­mate change re­search that might make a dif­fer­ence in the short term, this re­port may be more than just in­for­ma­tive. It might lead to ma­jor changes in their re­search. I see plenty of op­por­tu­ni­ties in this arena.

Fig.2. Con­cep­tual model of elec­tro­genic sul­fur ox­i­da­tion in aquatic se­di­ments by ca­ble bac­ter­ia. Source

Here's one ex­am­ple of where fun­da­men­tal mi­cro­bi­ol­ogy has led to a pos­si­ble methane-re­duc­ing ap­proach in rice cul­ti­va­tion. Rice is not only a very wa­ter-in­ten­sive crop; grow­ing it also re­leases a lot of methane. This is be­cause the wa­ter that nor­mally cov­ers the plant­ing ar­eas in tra­di­tional rice pad­dies pre­vents oxy­gen from get­ting into the soil, ren­der­ing it anoxic. Con­se­quently, methanogenic ar­chaea use the prod­ucts of or­ganic mat­ter de­com­po­si­tion – mainly in the form of ac­etate and hy­dro­gen – to make co­pi­ous amounts of methane that then seeps into the at­mos­phere. These methanogens do very well in the anoxic sub­soil where they are the most ef­fi­cient users of ac­etate and hy­dro­gen. There are plenty of pos­si­ble com­peti­tors present in those soils, but they do not have the sub­strate they need for en­ergy gen­er­a­tion. Sul­fate re­duc­ers are one class of such com­peti­tors. There­fore, the ad­di­tion of sul­fate to rice pad­dies in­deed al­lows the growth of sul­fate re­duc­ers. As they eas­ily out­com­pete methanogens, methane pro­duc­tion is greatly de­creased. The prob­lem is that added sul­fate does not last long as it is re­duced to sul­fide. Is there a way to cy­cle sul­fide back to sul­fate in the anoxic soil? Yes, there is. A re­cent pa­per shows that the sim­ple ad­di­tion of some very spe­cial bac­te­ria can lead to over 90% re­duc­tion in methane emis­sions from rice cul­ti­va­tion. Who are these bac­te­ria? The ca­ble bac­te­ria, de­scribed in a 2013 STC post. These Gram-neg­a­tive bac­te­ria grow as very long fil­a­ments, in the scale of sev­eral cen­time­ters. In­di­vid­ual cells are still only a few mi­crons each and bounded by their in­ner mem­brane and cell wall. But their outer mem­brane is con­tin­u­ous along the fil­a­ment. These bac­te­r­ial fil­a­ments can trans­fer elec­trons over cen­time­ter dis­tances, from sul­fide ox­i­da­tion at one end to oxy­gen re­duc­tion at the other end (Fig. 2.). In this man­ner ca­ble bac­te­ria cou­ple the pro­duc­tion of sul­fate in the anoxic soil with oxy­gen res­pi­ra­tion in the oxic re­gion. This is but one ex­am­ple of the many ways in which knowl­edge of mi­cro­bi­ol­ogy might be used in the fu­ture to re­duce methane emis­sions that re­sult from in­ten­sive agri­cul­ture.

What do the au­thors of this re­port think are the mit­i­ga­tion strate­gies that might have the most im­pact in the near fu­ture? In each of the ar­eas they cover, this is what they rec­om­mend:

En­teric Fer­men­ta­tion in Ru­mi­nants. En­teric fer­men­ta­tion ac­counts for a quar­ter of an­thro­pogenic CH4 emis­sions. Greater knowl­edge of the re­la­tion­ships among mi­cro­bial species in the ru­men mi­cro­biome will be nec­es­sary to ad­vanc­ing methanogen in­hibitors, ad­just­ing ru­mi­nant feed­stocks, and de­vel­op­ing vac­cines against ru­men methanogens.

An­i­mal Wastes. Over 10% of agri­cul­tural CH4 emis­sions comes from an­i­mal wastes and ma­nure man­age­ment. A bet­ter un­der­stand­ing of the ma­nure and soil mi­cro­biome from field ex­per­i­ments and mod­el­ing stud­ies will be im­per­a­tive for op­ti­miz­ing mi­cro­bial com­munities to re­duce CH4 emis­sions.

Rice Pro­duc­tion. As one of the top global food sta­ples, holis­tic re­search on the soil mi­cro­biome in re­la­tion­ship with the rice plant will be key to im­ple­ment­ing the ap­pli­ca­tion of mi­cro­bial in­oc­u­lants (such as ca­ble bac­te­ria), man­ag­ing al­ter­nate wet­ting and dry­ing strate­gies, and co-cul­tur­ing of rice and aquatic an­i­mals and al­ter­na­tive sub­strates to out­com­pete methano­gen­e­sis in rice pad­dies.

Land­fills. Land­fills are the third-largest source of hu­man-re­lated CH4 emis­sions in the U.S. Ex­panded char­ac­ter­i­za­tion of land­fill mi­cro­biome com­mu­nity struc­ture and func­tion, es­pe­cially with re­gard to plants in phy­to­cov­ers, will be im­por­tant when op­ti­miz­ing land­fill cov­ers that ef­fec­tively lower CH4 emis­sions. Ad­di­tion­ally, mi­cro­bial con­ver­sion of land­fill gas into valu­able prod­ucts will cre­ate fi­nan­cial in­cen­tives needed to in­crease re­search and de­vel­op­ment on mi­cro­bial so­lu­tions to ad­dress CH4.

We face ex­treme chal­lenges when it comes to green­house gas emis­sions. But chal­lenges al­ways bring up op­por­tu­ni­ties. One thing is clear from this list of rec­om­men­da­tions, there is no lack of op­por­tu­nity for in­no­v­a­tive mi­cro­bi­ol­o­gists to con­tribute to re­duc­ing methane emis­sions!

 

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