Category Archives: Environment
25th December 2018
Translated from the original article in Catalan.
We humans are destroying the planet Earth. Besides climate change (there are still ignorant people who do not believe it), the depletion of natural resources and the massive extinction of animal and plant species, one of the most visual effects is the coverage of the planet with rubbish. Since 71% of the surface is marine, most of the non-degrading waste finishes in the sea. In the oceans there are already large expansions covered by floating debris, especially plastics, called “plastic islands” (Figure 1). In the North Pacific area, where different sea currents come together, the “island” reaches 1500 km of radius, with plastics up to 200 meters deep, and continues to grow. There is more information of it, and also about the environmental consequences, in the Wikipedia article Great Pacific garbage patch.
Figure 1. Small portion of the Great Pacific Garbage Patch (From oceanandreserveconservationalliance.com)
Although there are many types of plastics, one of the most used and most abundant in waste and “plastic islands” is polyethylene terephthalate, known as PET or PETE (Figure 2). It is a type of thermoplastic polymer, vulgarly plastic, which belongs to the so-called polyesters, and is obtained by synthesis from petroleum. It is harmless, very resistant and lightweight and has multiple applications (Figure 3). Counting only bottles of PET for refreshing beverages, 1 million of them per minute are sold in the world. It is a recyclable material (see Pet bottle recycling in Wikipedia) but very resistant to biodegradation. In nature it can last some hundreds of years.
Figure 2. PET, polyethylene terephthalate.
Figure 3. Several applications of PET (From http://www.technologystudent.com).
PET is “eaten” by Ideonella sakaiensis
I. sakaiensis (Figure 4) are bacteria with rod shape, gram-negative, non esporulate aerobic heterotrophic, mobile with a flagellum, and catalase (+) and oxidase (+) (Tanasupawat et al 2016). They grow at neutral pH and are mesophilic, with optimum at 30-37°C. They belong to the phylogenetic group of betaproteobacteria, which include, besides many others, the known Neisseria (gonorrhoea and meningitis) and the nitrifying Nitrosomonas.
Figure 4. Scanning electron microscope images (false colour) of Ideonella sakaiensis cells grown on PET film for 60 h (From Yoshida et al 2016).
The 201-F6 strain, the first of the new species I. sakaiensis, was isolated from a landfill and identified in 2016 by a Japanese group of the Kyoto Institute of Technology that looked for bacteria using plastic as carbon source, from samples of remains of PET bottles (Yoshida et al 2016). They saw that these bacteria adhere to a low-grade PET film and can degrade it, by means of two enzymes characterized by these authors: a PETase and a MHETase, which produce terephthalic acid and ethylene glycol acid (Figure 5), which are benign environmental substances and that the bacteria can be metabolized. A colony of I. sakaiensis completely degraded a low-grade PET bottle in 6 weeks. High-grade PET products need to be heated to weaken them before the bacteria can degrade them. This is the first bacterium found as a PET degrader, and uses it as the only carbon source and energy source. Since PET has existed only for 70 years, these bacteria should have evolved in this short period until being able to degrade PET in a few weeks, instead of hundreds of years in nature (Sampedro 2016).
Figure 5. Predicted metabolic pathway of PET degradation by I. sakaiensis: extracellular PETase hydrolyses PET giving monohydroxyethyl terephthalic (MHET) and terephthalic acid (TPA). MHETase hydrolyses MHET to TPA and ethylene glycol (EG). The TPA is incorporated through a specific transporter (TPATP) and is catabolized to cyclohexadiene and this to protocatechuic acid (PCA) by the DCDDH. Finally, the PCA ring is cut by a PCA 3.4 dioxygenase with oxygen, as known for degradation of phenolic compounds and other xenobiotics. The numbers in parentheses are the ORF of the corresponding genes (From Yoshida et al 2016).
Previously, only some tropical microfungi (Fusarium solani) were known to degrade PET, and they also excreted esterases. In this case, Fusarium would be used to modify the polyester fabric, to achieve more hydrophilic and easier to work (Nimchua et al 2008). It is important to remember the structural similarity of synthetic PET fabrics (Figure 3) to those of natural fibre such as cotton, since these contain cutin, which is a polyester, a waxy polymer from the external parts of the plants. Therefore, the enzymes of Fusarium or Ideonella must be relatively similar to those that were already in nature long before the plastics were invented.
Recent genetic improvement of the enzyme PETase of Ideonella sakaiensis
In order to better understand the function and specificity of the PETase, a group of American and British researchers have recently characterized the structure of this enzyme (Austin et al 2018), mainly by high resolution X-ray crystallography, comparing it with a homologous cutinase obtained from actinobacteria Thermobifida fusca. The main differences between the two have been a greater polarization in the surface of the PETase (pI 9.6) than in the cutinase (pI 6.3), and on the other hand (Figure 6), a greater width of the active-site cleft in the case of PETase of I. sakaiensis. The cleft widening would be related with an easy accommodation of aromatic polyesters such as PET.
Figure 6. Compared structures (left) of the PETase of I. sakaiensis (above) and the cutinase of actinobacterium Thermobifida fusca (below), obtained by high resolution X-ray crystallography (0.92 Å). The active-site cleft is marked with a red dotted circle. Details (right) of the active site with different cleft widths in the PETase of I. sakaiensis (above) and the cutinase of T. fusca (below) are shown. (From Austin et al 2018).
Hypothesizing that the structure of the active site of the PETase would have resulted from a similar cutinase in an environment with PET, Austin et al (2018) proceeded to make mutations in the PETase active-site to make it more similar to cutinase and obtained a double mutant S238F/W159H which theoretically would make the entry of the active site closer (Figure 6). But their surprise was capital when they saw that the mutant degraded the PET better (an improvement of 20%), with an erosion of the PET film (Figure 7 C) even greater than the original PETase (Figure 7B). The explanation was that mutant changes in amino acid residues favoured PET intake in the active site, despite making a closest cleft (Austin et al 2018).
Figure 7. Scanning electronic microscopy images of a piece of PET without microorganisms (A), after incubating 96 h with PETase of the I. sakaiensis 201-F6 (B), and with PETase of the double-mutant S238F/W159H (C) (From Austin et al 2018).
In addition, these authors have shown that this PETase degrades also other similar semi aromatic polyesters, such as polyethylene-2,5-furonicarboxylate (PEF), and therefore this enzyme can be considered an aromatic polyesterase, but it does not degrade aliphatic ones.
The conclusion of their work is that protein engineering is feasible in order to improve the performance of PETase and that we must continue to deepen in the knowledge of their relationships between structure and activity for the biodegradation of synthetic polyesters (Austin et al 2018).
Other plastic-eating microbes ?
The discovery of I. sakaiensis has been very important for the possibility of establishing a rapid recycling process for PET, but it is not the first organism that has been found as plastic consumer. By the way, we can see the formulas of the main plastics derived from petroleum in Figure 8.
Figure 8. Formulas of the most common petroleum plastics: polyethylene (PE), polyvinyl chloride (PVC), polypropylene (PP), polystyrene (PS), polyethylene terephthalate (PET or PETE) and polyurethane (PU) (From Shah et al 2008).
Reviewing the bibliography, we see that many cases of plastic degrading microorganisms have been described (Shah et al 2008), especially polyethylene, polyurethane and PVC: various Pseudomonas, Rhodococcus and Comamonas among bacteria, and some Penicillium, Fusarium and Aspergillus between fungi.
Among the polyurethane consumers, mushrooms are highlighted (Howard 2002), and especially the plants endophyte Pestalotiopsis microspora, which can use polyurethane as the only source of carbon (Russell et al 2011).
On the other hand, the ability of the mealworms, the larval forma of the darkling beetle Tenebrio molitor, to chew and degrade the polystyrene foam is well known (Yang et al 2015). Fed only with the PS, these larvae degrade it completely in relatively short periods. As expected, the degradation of the PS is carried out by the intestinal bacteria of the animal (Figure 9). It has been demonstrated because degradation stops when administering antibiotics to the larva (Yang et al 2015). One of the isolated bacteria that has been shown to degrade PS is Exiguobacterium, from Bacillales group, but it is not the only one. In fact, when performing studies of metagenomics from gut of larvae eating PS, a large variety of bacteria have been found, and these vary depending on the kind of plastic, since the degradation of polyethylene has also been seen. Some of the bacteria with DNA found as predominant would be the enterobacteria Citrobacter and Kosakonia. It seems that the intestinal microbiota of Tenebrio is modified and adapted to the different ingested plastics (Brandon et al 2018).
Figure 9. Biodegradation of polystyrene by the intestinal bacteria of Tenebrio, the mealworm (Yang et al 2015).
Finally, as we see the microbial biodegradation of non-biodegradable or recalcitrant plastics should not surprise us, since on the one hand, there are natural “plastics” such as polyhydroxybutyrate or polylactic acid that are easily degradable (Shah et in 2008), and on the other hand the adaptive capacity of the microorganisms to be able to break the most recalcitrant chemical bonds is very large. Microbes evolve rapidly, and acquire better strategies to break the plastics made by humans (Patel 2018). We have seen in this case the degradation of PET, which in less than 70 years some microbes have already found a way to take advantage of it.
The problem is that we are generating too much plastic waste in no time and the microorganisms have not had time yet to degrade them. It is clear that we will have to help our microbial partners, not generating more degrading polymers, and recycling and degrading them, by using these same degrading microbes, among other ways.
Austin HP et al (2018) Characterization and engineering of a plastic-degrading aromatic polyesterase. Proc Nat Acad Sci 115, 19, E4350-E4357
Brandon AM et al (2018) Biodegradation of Polyethylene and Plastic Mixtures in Mealworms (Larvae of Tenebrio molitor) and Effects on the Gut Microbiome. Environ Sci Technol 52, 6526-6533
Howard GT (2002) Biodegradation of polyurethane: a review. Int Biodeterior Biodegrad 42, 213-220
Russell JR et al (2011) Biodegradation of polyester polyurethane by endophytic fungi. Appl Environ Microbiol 77, 17, 6076-6084
Sampedro J (2016 marzo 10) Descubierta una bacteria capaz de comerse un plástico muy común. El País
Shah AA et al (2008) Biological degradation of plastics: a comprehensive review. Biotechnol Adv 26, 246-265
Tanasupawat et al (2016) Ideonella sakaiensissp. nov., isolated from a microbial consortium that degrades poly(ethylene terephtalate). Int J Syst Evol Microbiol 66, 2813-2818
Yang et al (2015) Biodegradation and mineralization of polystyrene by plastic-eating mealworms: Part 2. Role of gut microorganisms. Environ Sci Technol 49, 12087-12093
Yoshida et al (2016) A bacterium that degrades and assimilates poly(ethylene terephthalate). Science 351,1196–1199
March 20th, 2016
The Arctic Ocean
Interestingly and coincidentally, “Arctic” comes from the Greek word αρκτος -arctos-, which means “bear” and is a reference to the constellation Ursa Minor, where is the North Star, which indicates the geographic North Pole .
The Arctic constitutes a unique ecosystem of the Earth, consisting of a large ice field, or ice-covered ocean, sometimes regarded as the northern part of the Atlantic Ocean, and it is surrounded by land, which is permafrost, with complete absence of trees. Life in the Arctic consists of organisms adapted to ice, including zooplankton and phytoplankton, fish, marine mammals, birds, land animals, plants and human societies fully adapted to the extreme conditions of the environment.
Due to global warming, isotherms are moving northward at a rate exceeding 50 km per decade over the past 30 years, so if we define the Arctic from a defined temperature or the tree line, its size is diminishing, being the reduction of sea ice the most visible effect.
Anthropogenic climate change: global warming, especially in the Arctic
Yes: climate change is here and it is generated by human activities, that is, it is anthropogenic. Previously there have been on Earth fluctuations in global temperature caused by natural phenomena, usually long-term and cyclical variations. For example, glaciations since about 2 million years are repeated every 100,000 years, and last ice age ended 15,000 years ago. So we are living now in an interglacial period and the next ice age could become not before 50,000 years. The cause of this cycle of glaciations seems to be orbital variations of the Earth, resulting in a lower insolation in high latitudes of the northern hemisphere during glacial periods.
Solar activity, like other stars, has cycles and roughly every 600 years there are periods of little activity (absence of very few solar spots and auroras), with lower energy output, which corresponds to cold periods in the Earth’s climate. The last minimal was in the period 1645-1715, and therefore from the middle of the eighteenth century we enjoy a maximum solar activity, with small cycles of minimum and maximum every 11 years.
Discounting these natural variations, it is clear that throughout the 20th century and especially since the 1960s there has been a steady increase in global average temperature (Figure 1), reaching almost 1ºC more than the beginning of the 20th century. In the early years of the current century the trend is worsening. The last 10 years have been the warmest since there are records, and the forecast is to continue increasing. Most experts agree that humans exert a direct impact on the heating process known as the greenhouse effect. The causes of this effect are some of gaseous components of the atmosphere, especially CO2, which has grown in parallel with rising temperatures, from about 300 ppm at the beginning of 20th century to nearly 400 ppm today. This CO2 and other gases as water vapour, methane and other exclusively anthropogenic absorb radiation and the result is that the atmosphere warms further.
Figure 1. Increase in average global temperature compared to the beginning of 20th century (from GISTEMP).
This global warming is particularly evident in the Arctic. The temperature increases are higher in northern latitudes, especially 60-70º N, where this past December 2015 (Figure 2) have raised to 9ºC above average in large areas of North America and Eurasia. This is called Polar Warming Amplification (PWA). The cause of this overheating in the Arctic respect of the rest of Earth is partly due to the loss of snow and ice (retroactive effect) because the largest area of land and water absorbs more solar energy than white ice (albedo effect), but also the PWA is partly due to the dynamic atmospheric transport, which transports heat energy from the clouds and subtropical regions to the north (Taylor et al 2013).
Figure 2. Thermal anomaly registered in December 2015 with respect to the average 1951-1980 (from GISTEMP).
Besides the consequences of this warming on the Arctic ice that we will comment below, another serious problem is the melting of permafrost, since then methane gas trapped under the frozen ground is released. This way, vast quantities of methane are released, and this greenhouse gas is contributing further to accelerate the global warming.
Less and less ice in the Arctic
Linear trends of sea ice extent and sea ice in the Arctic from 1979 to date are negative year after year, for any month is considered, but it is more clear by comparing Septembers, at the end of the summer when the ice is melting (Figure 3). Of the approximately 7 million km2 minimum in September (the maximum in March is about 16 million), about 100,000 km2 are melt per year, almost 9% every 10 years (Serreze et al 2007), so that there is now almost half ice than in 1979 (Figure 4).
Figure 3. Comparison of the extent of sea ice (in red): September 1979 and 2012 (from The Cryosphere Today).
Figure 4. Average monthly extension of Arctic sea ice since 1979 (Reeves et al 2013).
In addition to the reduction in surface ice, keep in mind the reduction in volume, representing now a third of what it was in September 1979.
There is a big difference between the different models for predicting the disappearance of Arctic sea ice. Half of them expect the total disappearance by September 2100. Predictions move since September 2040 the less optimistic until well past 2100 for the other (Serreze et al 2007).
Other problems resulting from the disappearance of sea ice are the ship traffic, which could shorten distances trips between the ports of northern countries, and on the other hand the exploitation of oilfields and other fossil fuels and minerals, since there is a large part of global reserves in the Arctic (Figure 5).
Figure 5. Left: forecast paths for open sea ships (blue) and for icebreakers (red) for 2040-2059. Right: Distribution of the potential major reserves of oil and gas (yellow) and licenses (red) and wells in operation or to operate (black). The dashed line indicates the limit of Conservation of Arctic Flora and Fauna (CAFF) declared by the Working Group of the Arctic Council (www.arctic-council.org). Figures from Reeves et al (2013).
Ecological consequences of the disappearance of the Arctic ice pack
There are many living beings linked to the ice. The polar bears roam on the Arctic ice, so we are feared for his fate. Many fish, seals and crustaceans (krill) form a food chain that starts from the algae that grow under the ice in a very consistent environment, rich in nutrients, especially favourable for marine life (Figure 6 A). Moreover, floating sea ice in summer is a good corridor for dispersion of terrestrial vertebrates (for instance arctic foxes) and plants.
The gradual disappearance of sea ice and warming in the Arctic coast involves a series of ecological imbalances (Figure 6 B). We see for example how walruses forced to remain grouped on the ground are more predisposed to disease transmission. The loss of sea ice diminishes dispersion by ice corridors and then the land populations are most isolated, thus gene flow is restricted. Polar bears and other predators that hunt on the sea ice have it much harder and their populations are at risk. Phytoplankton productivity decreases significantly, thereby reducing zooplankton, and then the whole food chain (fish, seals, etc.) is affected (Post et al 2013).
Figure 6. Ecological interactions influenced by sea ice. A: The distribution and seasonality of sea ice affects the abundance, distribution and interactions of the entire ecosystem in balance. B: The longest period without ice and less sea ice extent have disastrous consequences on the balance of the ecosystem (Post et al 2013).
The polar bear tries to survive
The polar bear (Ursus maritimus) is considered an endangered animal. There are only about 25,000 worldwide. The impact of climate change affects the exclusive habitat of polar regions and forecasts suggest that in a few years from now the ice of the Arctic will melt permanently and polar bears may become extinct because of warming area.
The polar bear is basically carnivorous, unlike others such as brown bears, and remains above the ice hunting seals. With the gradual disappearance of the ice it has more trouble finding preys, and some have begun to learn how to catch salmon rivers, as we see in the images (Figure 7).
Figure 7. White Bear dedicated to fishing salmons in order to survive (www.youtube.com/watch?v=9m_Q9Ojbcmw).
We have also seen groups of polar bears at sea fishing (see video) and dive emerging alternately as if they were dolphins or porpoises. Despite these small adaptations, the food is very low and it is clear that their populations are declining rapidly.
Orcas thrive north
The disappearance of the northern ice is a dramatic ecological change that is causing the disappearance of some species like the polar bear, but interestingly these imbalances benefit some other emerging species. This is the case of the killer whale (Orcinus orca), which is thriving more and more to the north (Figure 8).
Figure 8. Places (marked with numbers) of the Canadian Arctic where groups of orcas were repeatedly photographed between 2004 and 2009 (Young et al 2011).
Eskimo Inuit people live around the American Arctic (from Quebec to Alaska including Hudson Bay and adjacent islands) and the west coast of Greenland, and they are the first witnesses since the mid-twentieth century observing whales in their waters, unknown before. Moreover, in recent years scientists have made numerous orca’ sightings, they have been photographed individually (Young et al 2011), and their travels have been followed through bioacoustics (Ferguson et al 2010) and other techniques.
Figure 9. (Top): Narwhals with the characteristic great tusk, which gave rise to the myth of the unicorn. (Low): Group of orcas attacking narwhals cornered on the beach. Watch the video of PBS Nature.
For some years attacks by orcas on narwhals (as in Figure 9) have been observed repeatedly by Inuit Eskimos and studied in detail by several scientists. Laidre et al (2006) observed that before approaching whales, the narwhals tend to group, are more quiet and swim closer to the beach in shallow waters. During the attack, the narwhals disperse significantly but nevertheless mortality is very high. After predation, which can last several hours, oily stains are observed in sea surface, which come from fat of depredated narwhals (Figure 10).
Figure 10. Group of orcas surrounded by patches of oil on the sea surface from the fat of attacked narwhals (Laidre et al 2006).
Orcas’ attacks on narwhals are so common and effective that are beginning to affect the population. The effects are even worse in other cetaceans with smaller population such as whales of Greenland or bowhead (Balena mysticetus), which are now virtually extinct (Figure 11).
Figure 11. Scheme of preys’ proportions by a group of orcas from Hudson Bay (Ferguson et al 2010).
In conclusion, anthropogenic climate change is affecting the Arctic ecosystem severely (and all the other ecosystems), and although this problem is becoming known, effective policy measures to reduce emissions of CO2 and other greenhouse gases are so scarce that hardly will arrive in time. We are leading the planet Earth to a massive extinction of species and ecological changes ever seen in the history of humans.
The picture says it all: polar bear habitat is running out.
Arctic Council: http://www.arctic-council.org
Ferguson S.H., Higdon J.W. & Chmelnitsky E.G. (2010) The rise of killer whales as a major Arctic predator. In S.H. Ferguson, et al. (eds.): A little less Arctic: top predators in the world’s largest northern inland sea, Hudson Bay. Pp. 117–136. New York: Springer
GISTEMP, Goddard Institute for Space Studies Surface Temperature Analysis (NASA-GISS): http://data.giss.nasa.gov/gistemp/
Hawkings E (2014) nov 28: http://www.climate-lab-book.ac.uk/2014/hiatuses-in-the-rise-of-temperature/
Laidre KL, Heide-Jørgensen MP, Orr J (2006) Reactions of narwhals, Monodon monoceros, to killer whale, Orcinus orca, attacks in the Eastern Canadian Arctic. Can. Field Nat., 120, 457–465
Morell V (2012) Killer whale menu finally revealed. http://www.sciencemag.org/news/2012/01/killer-whale-menu-finally-revealed
Post et al. (2013) Ecological Consequences of Sea-Ice Decline. Science. DOI: 10.1126/science.1235225: http://www.carbonbrief.org/knock-on-effects-for-wildlife-as-the-arctic-loses-ice
Reeves RR et al (2014) Distribution of endemic cetaceans in relation to hydrocarbon development and commercial shipping in a warming arctic. Marine Policy 44, 375-389
Serreze MC, Holland MM, Stroeve J (2007) Perspectives on the Arctic’s shrinking sea-ice cover. Science 315, 5818, 1533–6.
Taylor PC, Cai M, Hu A, Meehl J, Washington W, Zhang GJ (2013) Decomposition of feedback contributions to Polar Warming Amplification. J Climate 26, 7023-43
The Cryosphere Today: http://arctic.atmos.uiuc.edu/cryosphere/
Young BG, Jeff W. Higdon JW, Steven H. Ferguson SH (2011) Killer whale (Orcinus orca) photo-identification in the eastern Canadian Arctic. Polar Research Vol 30
Nowadays there is more evidence that the bacteria found in the high troposphere (8-15 km) could influence the density of clouds and rain.
Firstly, we must remind that the troposphere is the lowest part of the atmosphere, and the 8-15 km layer is the high troposphere, near the tropopause that borders the stratosphere, above the Mount Everest. Here there are some of the highest clouds.
So, in a recent study (DeLeón-Rodríguez et al, 2013) it has been shown that the viable bacteria (by epifluorescence microscopy and quantitative PCR) at a 10 km altitude (samples taken above the Caribbean Sea and the Atlantic West) represent 20% of the particles with size between 0.25 and 1 mm, and bacteria are at least 10 times more abundant than fungi, with numbers of 105 per m3, with a 60% of viable cells. This suggests that bacteria are an important and underestimated fraction of microparticles of atmospheric aerosols, even at higher concentrations than lower altitudes.
The authors have analyzed the bacteria by pyrosequencing (Roche 454) the rRNA genes. They have seen that the tropospheric microbiome has a good variety of bacterial taxa that vary dynamically according to the atmospheric turbulence and in the presence of hurricanes. Some of the most abundant bacteria found are those using compounds C1-C4 (e.g., oxalic acid) present in the atmosphere, so these bacteria are metabolically active at these altitudes. This reinforces the idea of the active role of bacteria in the troposphere, and that there are not only inert spores (fungal) floating through the air.
In this sense, this metagenomic analysis also confirms the presence of bacteria that are able to catalyze the formation of ice crystals and hence the cloud condensation. This process of nucleation (ice nucleation, IN) occurs when the water molecules coalesce around a seed particle, for example dust. Depending on the temperature, these complexes can grow to become water droplets or ice, leading to the formation of rain or snow. Given that the high troposphere dust particles are scarce, it is evident the role of bacteria in this phenomenon.
One of the key roles in the nucleation of ice (IN) by bacteria is that they catalyze ice formation at temperatures close to 0°C, unlike the formation of ice nuclei by the inorganic particles, which is done at temperatures lower, below -10°C, and without any core particle the ultra-pure water freezes at -40°C.
Ice nucleation by bacteria has been reproduced in the laboratory (Christner et al, 2008) with samples of rain and snow from around the world (Canada, USA, Pyrenees, Alps and Antarctica), showing that in the samples treated with lysozyme (which hydrolyzes bacterial cell wall) or treated with heat, the IN activity was reduced almost 100% at a temperature of -5°C. Therefore, bacteria are responsible of the IN at these relatively high temperatures.
The bacteria most commonly associated with the IN activity are species associated with plants, such as Pseudomonas syringae or Xanthomonas campestris, which also often have been detected in atmospheric aerosols and clouds. P. syringae has also been found in the hail stones.
The phenomenon of IN by P. syringae was already observed in 1974 (Maki et al.) and after it has been shown (Gurian-Sherman & Lindow 1993) that IN strains of this species and others have in the outer membrane of the cell wall, as a active IN, a protein of 180 kDa, composed of repeats of a consensus octapeptide. This protein forms a planar arrangement that traps water molecules producing a mold for ice formation.
This feature makes that these bacteria are responsible for most of frost damage in plants, besides than P. syringae is pathogen of many plants at room temperature by the production of a compound (coronatin) who keeps the stomata open, causing the bacterial invasion of plant tissues (Nigel Chaffey, 2012).
Tomato leaf infected with Pseudomonas syringae (Alan Collmer, Cornell University/Wikimedia Commons)
Coming back to the frost damage, most plants can withstand up to -5°C without much damage if these bacteria are absent, but the presence of the IN protein-forming bacteria such as P. syringae in numbers of only 1000 cells by g of plant increases dramatically the damage by freezing. These damages also facilitate the penetration of bacteria and infection.
Frozen plant (MO Plants& Maureen Gilmer)
This feature of ice nucleation by P. syringae is also utilized for the production of artificial snow. Although this can be made usually by the forced expansion of a pressurized mixture of water and air under appropriate conditions of temperature and humidity (e.g. ≤ 2°C at 20% humidity, or ≤ -2°C at 60%), snow production is favoured by the addition of nucleation agents, which can be inorganic, organic or the mentioned bacterial protein.
Coming back to the clouds, we must remind that bacteria are far less the sole agents of nucleation forming condensation droplets resulting in rain or snow. The cloud condensation nuclei, CCN, also called cloud seeds, can be very different types of microparticles of sizes around 0.1 – 1 mm. When this aerosol of microdroplets is condensed, it forms drops of 0.02 mm in the clouds, which give falling raindrops of 2 mm.
The microparticles are mostly of natural origin such as dust, sea salt, volcanic sulphates or organic microparticles result of the oxidation of volatile compounds. Some of these may be of industrial origin, as well as soot and other particles resulting from combustion. Another important biological source of CCN is the aerosols of sulphate and methanosulphate produced from dimethyl sulphur, which is made by phytoplankton in the oceans.
Anyway, despite atmospheric microbiology is still in its infancy, as we have seen there are more and more data on the importance of bacteria and other microorganisms on bioprecipitation of rain and snow. To find out more about their role, research must go beyond the description of the abundance of microorganisms in the atmosphere, and to understand the biological, physical and chemical properties of the transport processes involved. This will require interdisciplinary approach seemingly different disciplines such as oceanography, bacterial genetics and physics of the atmosphere, for example.
Chaffey N. (2012) COR, nice one, Mr Microbe !. AoB Blog.
Christner B. et al. (2008) Geographic, seasonal, and precipitation chemistry influence on the abundance and activity of biological ice nucleators in rain and snow. PNAS 105, 48, 18854-18859.
DeLeón-Rodríguez N. et al. (2013) Microbiome of the upper troposphere: species composition and prevalence, effects of tropical storms, and atmospheric implications. PNAS 110, 7, 2575-2580.
Gurian-Sherman D. & S.E. Lindow (1993) Bacterial ice nucleation: significance and molecular basis. FASEB J. 7, 14, 1338-1343.
Hardy J. (2008) The rain-making bacteria. Micro-Bytes.
Maki L.R. et al.(1974) Ice nucleation induced by Pseudomonas syringae. App!. Microbiol. 28, 456-460.
Morris C.E. et al. (2011) Microbiology and atmospheric processes: research challenges concerning the impact of airborne micro-organisms on the atmosphere and climate, Biogeosciences 8, 17-25