Team:Braunschweig/Project-content

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Nitrous Oxide, like carbon dioxide, is also naturally present in the atmosphere as it is part of the global nitrogen cycle: Nitrogen circulates between the atmosphere, plants, animals and bacteria breaking it down in the oceans and soils. Even though it has a variety of natural sources, human activities such as wastewater management or nitrogen fertilization increase the amount of nitrous oxide in the atmosphere. These molecules stay in the atmosphere for about 120 years but can be removed by certain types of bacteria or even destroyed by chemical reactions or ultraviolet radiation.
Nitrous Oxide, like carbon dioxide, is also naturally present in the atmosphere as it is part of the global nitrogen cycle: Nitrogen circulates between the atmosphere, plants, animals and bacteria breaking it down in the oceans and soils. Even though it has a variety of natural sources, human activities such as wastewater management or nitrogen fertilization increase the amount of nitrous oxide in the atmosphere. These molecules stay in the atmosphere for about 120 years but can be removed by certain types of bacteria or even destroyed by chemical reactions or ultraviolet radiation.
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In contrast to other greenhouse gases, fluorinated gases do not have natural sources and only arise from human activities. F-gases are emitted through different industrial processes and many of them have a very high global warming potential in comparison to other greenhouse gases. Therefore, even very small atmospheric concentrations can have great effects on global temperatures. Additionally they have very long atmospheric lifetimes, lasting up to thousands of years. F-gases are removed from the atmosphere only when they get destroyed by sunlight in the far upper atmosphere. In general, fluorinated gases are the most potent and longest lasting sort of greenhouse gases emitted by humans.
In contrast to other greenhouse gases, fluorinated gases do not have natural sources and only arise from human activities. F-gases are emitted through different industrial processes and many of them have a very high global warming potential in comparison to other greenhouse gases. Therefore, even very small atmospheric concentrations can have great effects on global temperatures. Additionally they have very long atmospheric lifetimes, lasting up to thousands of years. F-gases are removed from the atmosphere only when they get destroyed by sunlight in the far upper atmosphere. In general, fluorinated gases are the most potent and longest lasting sort of greenhouse gases emitted by humans.
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Methane is the second most important greenhouse gas. It is emitted by several natural sources such as wetlands but also by different human activities like leakage from natural gas and livestock farming. Methane can be removed from the atmosphere by natural processes in soil and chemical reactions in the atmosphere. As its lifetime in the atmosphere is, compared to other greenhouse gases, quite short (~12 years), targeting methane emissions as a means of reducing the overall greenhouse gas emissions in a relatively short period of time is a reasonable approach to reduce global warming. <br>
Methane is the second most important greenhouse gas. It is emitted by several natural sources such as wetlands but also by different human activities like leakage from natural gas and livestock farming. Methane can be removed from the atmosphere by natural processes in soil and chemical reactions in the atmosphere. As its lifetime in the atmosphere is, compared to other greenhouse gases, quite short (~12 years), targeting methane emissions as a means of reducing the overall greenhouse gas emissions in a relatively short period of time is a reasonable approach to reduce global warming. <br>

Revision as of 09:26, 14 October 2014

E. Cowli - Fighting Climate Change - iGEM 2014 Team Braunschweig

Hier fehlt der Header

Problem

That's why we Target Methane

Problem

Gases absorbing and emitting radiation within the thermal infrared range in the atmosphere are called greenhouse gases. They are responsible for the greenhouse effect. The main greenhouse gases are carbon dioxide, methane, nitrous oxides and fluorinated gases or, in short, F-gases.
The relative contribution of each of these greenhouse gases to climate change depends roughly on three main factors:

1. The amount of a respective gas in the atmosphere.
2. The duration of stay in the atmosphere.
3. The intensity of their impact on the global temperature.

For each of these gases a Global Warming Potential (GWP) has been calculated which is a measure of the total energy that a gas absorbs over a particular period of time compared to carbon dioxide. Besides, it is also based on the degradation rate of the respective gas. Thus the GWP describes the ability of a gas to trap heat in the atmosphere. The larger the GWP the bigger the effect of the particular gas on global warming.
As shown in the figure below, the GWPs (100 years) of the primary greenhouse gases differ significantly. Since the GWP is calculated in relation to carbon dioxide, the GWP of carbon dioxide is defined as 1. The 100 year GWP for methane is 25 implying that methane will trap 25 times more heat than carbon dioxide over the next 100 years.

Problem

Carbon dioxide is the main greenhouse gas emitted by human activities. As part of the Earth’s carbon cycle, carbon dioxide is also naturally present in the atmosphere: It is constantly exchanged between the atmosphere, ocean and land surface as it is produced and absorbed by many microorganisms, plants and animals. But human activities affect the carbon cycle by adding more carbon dioxide to the atmosphere and by damaging natural sinks, for example forests which would otherwise remove carbon dioxide from the atmosphere.

Nitrous Oxide, like carbon dioxide, is also naturally present in the atmosphere as it is part of the global nitrogen cycle: Nitrogen circulates between the atmosphere, plants, animals and bacteria breaking it down in the oceans and soils. Even though it has a variety of natural sources, human activities such as wastewater management or nitrogen fertilization increase the amount of nitrous oxide in the atmosphere. These molecules stay in the atmosphere for about 120 years but can be removed by certain types of bacteria or even destroyed by chemical reactions or ultraviolet radiation.

Problem

In contrast to other greenhouse gases, fluorinated gases do not have natural sources and only arise from human activities. F-gases are emitted through different industrial processes and many of them have a very high global warming potential in comparison to other greenhouse gases. Therefore, even very small atmospheric concentrations can have great effects on global temperatures. Additionally they have very long atmospheric lifetimes, lasting up to thousands of years. F-gases are removed from the atmosphere only when they get destroyed by sunlight in the far upper atmosphere. In general, fluorinated gases are the most potent and longest lasting sort of greenhouse gases emitted by humans.

Methane is the second most important greenhouse gas. It is emitted by several natural sources such as wetlands but also by different human activities like leakage from natural gas and livestock farming. Methane can be removed from the atmosphere by natural processes in soil and chemical reactions in the atmosphere. As its lifetime in the atmosphere is, compared to other greenhouse gases, quite short (~12 years), targeting methane emissions as a means of reducing the overall greenhouse gas emissions in a relatively short period of time is a reasonable approach to reduce global warming.
Globally around 60% of all methane emissions originate from human activites like industry, agriculture and waste management.

Even though the total methane emissions decreased by around 10% between 1990 and 2012 the emissions associated with agricultural activities did not. This is mostly due to the intensification of livestock farming. Methane is set free in the course of digestion in ruminant animals like cattle and emitted into the atmosphere. Therefore, by increasing livestock production methane emissions are increased as well.

Problem

Methane is formed in a process called methanogenesis which, for example, takes place in the rumen of cattle. However, the methane is not further utilized by any of the microorganisms living in the animal’s digestive tract nor by the animal itself, so it gets exhaled to the atmosphere and thus contributes to global warming. Read here (LINK) what has been done in the past against these emissions, or here (LINK) how exactly methanogenesis takes place.

Origin of Methane

Problem

Methane from biological sources can originate in various different environments like peat bogs, deep-sea hydrothermal vents and the digestive tracts of animals. Despite this variation there are certain common aspects: All biologically formed methane originates from methanogenic archaea and all these methanogens are strictly anaerobic organisms [1]. However, there is not only one mode of methanogenesis. Some methanogens perform hydrogenotrophic methanogenesis which mostly relies on the reduction of carbon dioxide while hydrogen usually acts as the electron donor. The methylotrophic methanogens, in contrast, are additionally able to use a variety of other compounds for methane generation, for example certain methyl compounds. Lastly, in acetoclastic methanogenesis acetate is used as a substrate for methane formation [2,3]. Hydrogenotrophic methanogens comprise, for example, the order Methanobacteriales and species like Methanobrevibacter ruminantium. Methanosarcinales is the most important order of the methylotrophic methanogens with species like Methanosarcina barkeri. Representatives of both orders and both modes of methanogenesis can be found in the rumen of cattle, one of the most important biological methane sources [4]. In the hydrogenotrophic pathway carbon dioxide is initially reduced with electrons taken from the oxidation of hydrogen or alternative electron donors. The resulting formyl group is then subsequently reduced. Involved in this process are several unique cofactors to which the groups of the different oxidation states - some of them cyclic - are being bound until methane is released. The reduction reactions are coupled to the export of sodium ions across the cell membrane. The methylotrophic pathway, in which C1 compounds like methanol or methylamines can be utilized, joins the hydrogenotrophic pathway at a late stage. A total of four C1 molecules is needed here, one of which is oxidized to provide electrons for the reduction of the other three. In the acetoclastic pathway the electrons required for reduction are taken from the oxidation of the carbonyl carbon of acetate [2,3].

Digestion in Ruminants

Like all ruminants, cattle are herbivores, which means that they mainly feed on plants – the most demonstrative example for this might be a cow grazing on a meadow. For the vegetable components to be properly utilized, however, the cow needs a stomach completely different from the kind you find in other mammals like, for example, humans. Indeed, the stomach of ruminants consists of four components: rumen, reticulum and omasum are succeeded by the abomasum, and those four compartments work closely together in the digesting process. Thanks to this, the grazing cow is able to utilize cellulose in order to gain energy, which is not possible for most other mammals.

When a cow ingests food, the latter is swallowed without being chewed at first, passes through the reticulum and enters the rumen. Here, fermentation is carried out by microorganisms, which can take 20 to 50 hours. Next, small balls are formed from the processed food in the reticulum by muscle contractions, and these balls are regurgitated, chewed and mixed with saliva. The resulting food mush is then swallowed once again; this time, though, it does not enter the rumen after passing the reticulum, but is channelled into the omasum. Thus, the reticulum works as a kind of filter separating the unprocessed food of the first swallowing from the processed mush of the second.

The importance of the rumen in digestion arises from the numerous microorganisms living in it. In fact, each gram of rumen contents contains about 1010 to 1011 bacteria belonging to 300-400 different species, resulting in a great variety of metabolic profiles. Most of these organisms are obligate anaerobes, meaning that they can only survive and grow in the absence of oxygen. However, a certain amount of oxygen entering the rumen with every swallow can hardly be prevented; thus, there are also a few facultative anaerobes present capable of consuming oxygen.

Among the billions of microorganisms in the rumen there are different groups specialized on degrading compounds like cellulose, starch, or lactate. The sugars set free by breaking down these substances are subsequently fermented. The size and structure of the rumen ensures that the food is properly mixed and that the microorganisms can work on it for a sufficiently long time. During this process different kinds of gases originate. The so-called volatile fatty acids (VFAs) like acetic, propionic, and butyric acid are particularly important for the animal, as they pass through the rumen wall into the bloodstream, serving as a main source of energy. Unfortunately, alongside the VFAs greenhouse gases like carbon dioxide and methane are produced and released into the atmosphere by eructation.

All rumen microbes are well adapted to the conditions prevailing in this special ecosystem. Its temperature averages at about 39°C, but is also dependent on external influences.The pH value is relatively constant, ranging between about 6.5 and 7.0, although acids are permanently produced – this constancy is due to bicarbonate contained in and swallowed with the saliva and to ammonium set free in the course of the deamination of amino acids. Under certain nutritional conditions, though, stronger deviations of the pH value may occur due to the rapid proliferation of bacteria like Streptococcus bovis which produce lactic acid.

In newborn ruminants the microflora and -fauna of the rumen is not yet properly developed. However, through contact with the mother animal or aerosols a rapid colonization occurs and a microbial population emerges, ensuring the functionality of the rumen. In the view of this it is imaginable to influence the fermentation processes in the rumen by dispensing microbial probiotics to the calf directing the composition of the population in a certain way. Furthermore, there are different approaches to particularly influence methane production inside the rumen by dispensing so-called direct-fed microbials (DFM); these are, however, as yet restricted to making use of alternative metabolic pathways competing with methanogenesis.

  1. Hristov AN, Oh J, Firkins JL, Dijkstra J, Kebreab E, Waghorn G, Makkar HP, Adesogan AT, Yang W, Lee C, Gerber PJ, Henderson B, Tricarico JM (2013) Special topics – Mitigation of methane and nitrous oxide emissions from animal operations: I. A review of enteric methane mitigation options. J. Anim. Sci. 91(11):5045-69
  2. Jeyanathan J, Martin C, Morgavi DP (2014) The use of direct-fed microbials for mitigation of ruminant methane emissions: a review. Animal 8(2):250-61
  3. Madigan MT, Martinko JM, Stahl DA, Clark DP (2012) Brock Biology of Microorganisms. 13th ed. San Francisco: Pearson Education. pp. 762-6
  4. Weimer PJ (1992) Cellulose Degradation by Ruminal Microorganisms. Crit Rev Biotechnol 12(3):189-223

Idea

That's what we are going to do?

The Greenhouse Effect is a well known phenomenon describing the synergy of several gases in the atmosphere of our earth, which leads to positive as well as negative consequences. Without greenhouse gases the earth would be a very cold place and life would not be possible the way we know it. Nevertheless, due to increasing emission of gases like methane and carbon dioxide the effect is further enhanced and thus causes global warming. Among other things the greenhouse gas methane is a product of the natural digestion of cows. Because the consumption of dairy products and meat is increasing mass husbandry is widely spread. Hence, the emission of methane attributed to cows rises to unnatural dimensions. Since most people are not willing to change their daily nutrition and reduce their consumption of several products significantly (see our survey) an elimination of methane emissions caused by cows would be useful. However, former approaches merely regard either the methanotrophs responsible for methane production or the substrates they need. Our project idea is to reduce global methane emission right at one of the sources, the rumen of cows, without affecting resident organisms. Our idea is to provide the digestive tract with a specially modified microorganism, named E. cowli, which is planned to metabolise the methane before its emission and, therefore, prevents the enhanced greenhouse effect and global warming.

Approach

Approach

Past Approaches

Past strategies for reducing the methane emissions from ruminants like cattle can be subdivided into two main approaches: Firstly, approaches aimed directly at the methanogens, and secondly, approaches aimed at other microorganisms of the rumen which provide the methanogens with substrates for methanogenesis [1]. The methanogens engaged in such symbioses are also called protozoa-associated methanogens (PAMs) and account for about 37% of the methane produced in the rumen [2].
The substrates for methanogenesis vary greatly among different methanogenic organisms because they use different modes of methanogenesis. For example, the archaeon Methanobrevibacter ruminantium (order Methanobacteriales) utilizes carbon dioxide, hydrogen and formate for methane production, whereas Methanosarcina barkeri (order Methanosarcinales) can grow on a wider range of substrates like acetate or methylamines, in addition to hydrogen and carbon dioxide [1]. One obvious approach for the reduction of methane emissions is changing the diet fed to the animal. For example, the amount of methane emitted by cattle is lower when the diet consists mostly of concentrate, which is rich in nutrients and low in fibre content, rather than a mixture of concentrate and forage [3]. Another possibility is grinding the food before feeding so that it resides in the rumen for a shorter period. This way, there would be less time for the microorganisms, including methanogens, to work on the food [1]. Apart from the type of food, the latter can also be supplemented by, for example, fatty acids which would then inhibit the protozoa associated with the methanogens. To this aim, it was found that medium-chain saturated fatty acids with chain lengths of 8-10 are most effective [4]. However, the use of unsaturated fatty which can act as hydrogen sinks and thus inhibit methanogenesis is also discussed [1]. Another approach by which the association between protozoans and methanogens may be split is defaunation, i.e. the removal of the protozoans from the rumen. As a large amount of methane emissions is accounted for by PAMs, this treatment would act on an equally large source of methane emissions [1,2].
There have also been vaccines developed in order to stimulate the ruminant’s immune system so that it acts on the methanogens [1]. However, such vaccines are usually directed against certain groups of methanogens only. In some cases, this might give those methanogens responsible for most of the emissions an advantage and thus increasing methane emissions instead of decreasing them [5].
Aside from the above-mentioned ones there are several further attempts to stop methane emissions in the rumen, but it also has to be considered that although by the release of methane from the rumen a substantial amount of energy is lost, methanogenesis still has a point in ruminal ecology. The removal of hydrogen prevents inhibition of the fermentative processes which are essential for the cattle’s digestion [6]. Therefore, decreasing the rate of methanogenesis might be positive for the climate, but probably not so for the cattle’s digestion. In contrast, no such disadvantages come along with our idea of degrading methane because methanogenesis itself would not be prevented. Therefore, the methanogens could still fulfill their important role in the cattle’s digestion. As the methane is not further utilized anyway, degrading it should not cause any damage to the animal.

  1. Hook SE, Wright ADG, McBride BW (2010) Methanogens: Methane Producers of the Rumen and Mitigation Strategies. Archaea 2010:ID 945785
  2. Belanche A, de la Fuente G, Newbold CJ (2014) Study of methanogen communities associated with different rumen protozoal populations. FEMS Microbiol Ecol [published ahead of print] doi: 10.1111/1574-6941.12423
  3. Rooke JA, Wallace JJ, Duthie CA, McKain N, Motta de Souza S, Hyslop JJ, Ross DW, Waterhouse T, Roehe R (2014) Hydrogen and methane emissions from beef cattle and their rumen microbial community vary with diet, time after feeding and genotype. Br J Nutr 112:398-407
  4. Dohme F, Machmüller A, Wasserfallen A, Kreuzer M (2001) Ruminal methanogenesis as influenced by individual fatty acids supplemented to complete ruminant diets. Lett Appl Microbiol 32:47-51
  5. Williams YJ, Popovski S, Rea SM, Skillman LC, Toovey AF, Northwood KS, Wright AD (2009) A Vaccine against Rumen Methanogens Can Alter the Composition of Archaeal Populations. Appl Environ Microbiol 75:1860-6
  6. Sharp R, Ziemer CJ, Stern MD (1998) Taxon-specific associations between protozoal and methanogen populations in the rumen and a model rumen system. FEMS Microbiol Ecol 26:71-8
ERN ERN ERN

Solution

Methanotrophs

Methanotrophic bacteria accomplish the remarkable task of utilizing the inert compound methane as their sole source of carbon and energy. They are usually found where anaerobic and aerobic environments come together, the former providing methane and the latter oxygen. They use methane by oxidizing it to methanol, which is then further converted to formaldehyde and can be assimilated into the cellular biomass [1,2].
Methanotrophs can be subdivided into two classes which are classified mainly by phylogenetic analyses, but also by physiological and morphological differences. Type I methanotrophs belong to the γ-Proteobacteria, while type II methanotrophs are members of the α-Proteobacteria. They differ in the way the assimilation of formaldehyde, subsequent to methane oxidation, takes place [3].

Methylococcus capsulatus, a type I member, is considered a model methanotroph and has been extensively studied in recent years [4]. However, due to several characteristics it is much harder to handle than other model organisms like, for example, Escherichia coli. M. capsulatus is thermophilic with a temperature optimum of 45°C and has a rather slow growth rate . Therefore, it would be useful if enzymes like those catalyzing the degradation of methane could be expressed in an organism more easy to handle - not only for research but also for industrial purposes.

  1. Dalton H (2005) The Leeuwenhoek Lecture 2000: The natural and unnatural history of methane-oxidizing bacteria. Phil Trans R Soc 360:1207-22
  2. Merkx M, Koop DA, Sazinsky MH, Blazyk JL, Müller J, Lippard SJ (2001) Dioxygen Activation and Methane Hydroxylation by Soluble Methane Monooxygenase: A Tale of Two Irons and Three Proteins. Angew Chem Int Ed 40:2782-807
  3. Ward N, Larsen Ø, Sakwa J et al. (2004) Genomic Insights into Methanotrophy: The Complete Genome Sequence of Methylococcus capsulatus (Bath). PLoS Biol 2:e303
  4. Hakemian AS, Rosenzweig AC (2007) The Biochemistry of Methane Oxidation. Annu Rev Biochem 76:223-41

Results

Benjamin

In August we had a visitor in our lab for two weeks. Benjamin, a pupil from a local school, had decided to expand his knowledge on Synthetic Biology and Biotechnology. He proved to be very keen to learn new things and to become a valuable (albeit short-term) member of our team. Here is how he evaluates his stay with us:
“During the past two weeks I did an internship at the Institute for Biochemistry, Biotechnology and Bioinformatics of the TU Braunschweig. It was unique in several ways: I had the opportunity to look over the iGEM team members’ shoulders, to ask questions and I could even contribute to their project by carrying out some smaller tasks. These two weeks were eventful and exciting for me and I do not regret investing part of my holidays for them. I got a great insight into Biotechnology, especially the lab work.”
And although he may be a little too young for iGEM, he still acquired a taste for the idea behind the competition: “Concerning iGEM, I am particularly fascinated by the fact that the project is in the students’ hands from start to finish and that they can get so much out of their contribution. Maybe I will also take this direction later and take part in the competition… Lots of luck to the Braunschweig iGEMers and I keep my fingers crossed for E. cowli to eventually be able to degrade methane. THANK YOU for the great internship!”

Benjamin Benjamin Benjamin

Potential Impact

Survey1

Recent reports show that the public interest in vegan diets is on the rise [1]. Indeed, if more people forwent consuming beef and dairy products, methane emissions caused by livestock farming could be drastically reduced. In order to get further insight into the public’s willingness to change their diet for the sake of the climate we conducted a survey - before the revelation of our project, so that they would not be influenced. The exact question was: “Could you imagine changing your nutrition such that there are no more dairy or beef products on the menu to reduce the output of greenhouse gases?” The results are shown in the diagram at the left.
Even confronted with the possible consequences of their consume of dairy and beef products, most people were not willing to change their nutrition for a better climate. Additionally, it should be considered that clicking “Yes” in a survey is probably much easier than turning something into action for real, so in reality the “No” fraction would probably even more numerous. This implements that there should be another way of reducing the greenhouse gas emissions caused by livestock, and with our project we want to show how this could be achieved.

Engineering Principles

Engineering Principles

While planning our project and putting it into practice we always kept in mind some fundamental principles of engineering. Firstly, our project was well planned and all available information was collected and evaluated beforehand, allowing us to adjust our construct before actually starting in the wet lab. Also, we kept the whole construct as simple and made use of as many standard biobricks from the iGEM registry as possible. Those parts not available in the registry (see our new parts) were built into the assembly standard making them available to all users of the Registry of Standard Biological Parts.
Additionally, we ensured the functionality of each subunit by building His­ constructs of all mmo genes in order to test them separately. This allowed us to evaluate their functionality and, if necessary, to adjust them for a better performance. Furthermore, as it is the duty of an engineer to not only take responsibility for the positive but also the negative consequences of a construction, we never left safety and ethics out of our equations.

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