Properties of the engine oils
\r\n\tAn important component of this book must be dedicated to the more recent treatments namely with biologic therapies but focusing also on new small molecule inhibitors and experimental therapies.
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He has more than 20 years of research experience in the development of optical fiber devices including fiber amplifiers, fiber lasers, and fiber optic sensors. Professor Harun has published more than 900 articles in reputable ISI journals, and his papers have been cited more than 8000 times with an h-index of more than 40, showing the impact on the community. 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Presently, two-stroke engines are commonly used in motorcycles, scooters, chainsaw, agricultural machinery, railways grinding machines, outboard applications, etc.
Usually, the moving parts of a two-stroke motor are lubricated either by using mixture of oil with fuel or by pumping oil from a separate tank. Both designs use total-loss lubrication method, with the oil being burnt in the combustion chamber. Therefore, the lubricating oil must meet specific requirements: it must have an optimal balance of light and heavy oil components to lubricate at high temperature, it must produce no deposits (carbon sooty and other) on moving parts, and it should be ash-less. In addition, the oil should provide good protection of moving parts at high speed under deceleration of engine with the throttle closed, when the engine usually suffers from oil-starvation.
Also, two-stroke engine produce more contaminants than four-stroke engines, due to oil burning in the combustion chamber. Therefore, it is very important to reduce these contaminations to meet ecological requirements.
Most challenging issue of the European technological strategy resides in complete substitution of fossil-based fuels and lubricating oils with renewable eco-friendly and high performance materials. Esters and polyglycols were identified as alternative base oils because of their high biodegradability, low toxicity; low ash formation and absence of polymer components, in [1]. Synthetic esters are characterized by their polar structure, high wear resistance, good viscosity-temperature behaviour, miscibility with non-fossil fuels. Esther-base oils can be blended with various components like antifoam agents, oxidation inhibitors, pour-point depressants, antirust agents, detergents, anti-wear agents, friction reducers, viscosity index improvers, etc., to create environmental friendly prototype engine oils and to meet the changing environmental requirements in low sulphur fuels and other alternative fuels and their application to engine oils.
Low metal additives content and clean-burnt characteristics result in less engine fouling with much reduced ring stick and lower levels of dirt built-up on ring grooves, skirts and under crowns. Owing to the presence of polar ester groups in the molecule which have higher adhesion to metal surface, esters have much better lubricity than hydrocarbons. The performance of the ester-based lubricating oils can be further improved by selecting a proper base oil and additive package.
Another important problem is related with performance of fuel injector system when bio fuels are used. Diesel injection nozzles consist of a body (usually in Ni-Cr steel) and needle valve (High speed steel, HSS), fitted together with very strict tolerances. The design of the nozzle, i.e., the number of orifices, their diameters, positions and drilling angles depend on specific engine application. The current trend is to use multi-hole nozzles with very small holes with diameter of only 0.10 - 0.14 mm in order to improve the fuel atomization and flow pattern.
Heat treatments are applied to the body and the needle to obtain the necessary hardness both on the surface and in the core of the parts and to face the following problems:
fatigue failures at high stress areas due to repeated pulses of very high injection pressures;
thermal shocks.
Adequate finishing of the orifice surfaces is very important also to optimize the erosion resistance.
The usage of new diesel blends characterized by different physical and chemical properties as compared with the traditional fuels could lead to modifications both in the choice of materials, geometry and positioning of orifices or their surface finishing to ensure the correct spray pattern. This work describes the results of our recent studies aimed at solving the problems related to the introduction of new eco-friendly oils and lubricants.
Three different synthetic ester base oils have been selected to formulate three prototype engine oils with the same additive composition. These oils are different mixtures of fully saturated polyglicol-ester and mono-ester types and designated as SEMO 4, SEMO 5 and SEMO 10. Same additive package has then been added to the three bases. After comparative characterization of these prototype oils and selection of the oil with the best tribological performance (SEMO 10), a new improved formulation was developed based on the selected lubricating oil, designated SEMO 36. In addition, conventional mineral oil for two-stroke engines was used as reference oil. The additive package composition of the reference oil is different but it is ash-free as well as the other SEMO oils.
Oil viscosity was characterized according to ASTM D-445-06 standard procedure in [3], and viscosity index was determined using ASTM D-2270-04 in [4].
Deposit forming tendency of the oils was characterized by the Coker test at 250 °C during 12 h. Some physical and rheological properties of the lubricating oils are shown in Table 1. Among the prototype lubricating oils, SEMO 10 has the lowest viscosity both at 40 and 100 °C, the highest flash point and the lowest deposit forming tendency.
Unleaded petrol (E228) and bioethanol E85 (mixture of 85% of ethanol with 15% of gasoline) were selected to test miscibility of the lubricating oils with standard and alternative fuels. For this purpose two different lubricant/fuel ratios were used. Regarding to the miscibility method A (90% lubricant in fuel), SEMO 10 as well as SEMO 5 demonstrated good miscibility both with unleaded petrol and E85. Compared to this, the results for the 2% mixtures according (method B) differed. All tested lubricants proved to be perfectly miscible with EN228 fuel, whereas only SEMO 36 demonstrated to be fully miscible with E85. According to both miscibility methods the reference oil was only miscible with EN228. SEMO 36, when compared to its original prototype SEMO 10, has a much higher viscosity. Flash point for this lubricant is lower than for SEMO 10 but still higher than 200 °C.
\n\t\t\t | \n\t\t\t | \n\t\t\t\t | \n\t\t\t\n\t\t\t\t | \n\t\t\t\n\t\t\t\t | \n\t\t\t\n\t\t\t\t | \n\t\t\t\n\t\t\t\t | \n\t\t
Density, g/ml | \n\t\t\t0.877 | \n\t\t\t0.915 | \n\t\t\t0.917 | \n\t\t\t0.935 | \n\t\t\t0.999 | \n\t\t|
Viscosity @ 40ºC,mm | \n\t\t\t59.5 | \n\t\t\t84.9 | \n\t\t\t94 | \n\t\t\t45.8 | \n\t\t\t113.3 | \n\t\t|
Viscosity @ 100ºC, mm | \n\t\t\t8.6 | \n\t\t\t12.5 | \n\t\t\t13.2 | \n\t\t\t8.0 | \n\t\t\t18.3 | \n\t\t|
Viscosity index | \n\t\t\t117 | \n\t\t\t144 | \n\t\t\t140 | \n\t\t\t147 | \n\t\t\t181 | \n\t\t|
Flash point, ºC | \n\t\t\t120 | \n\t\t\t204 | \n\t\t\t190 | \n\t\t\t260 | \n\t\t\t218 | \n\t\t|
Pour Point, ºC | \n\t\t\t-21 | \n\t\t\t-39 | \n\t\t\t-33 | \n\t\t\t-39 | \n\t\t\tnot tested | \n\t\t|
Deposit forming * | \n\t\t\t9 | \n\t\t\t4 | \n\t\t\t3 | \n\t\t\t9 | \n\t\t\tnot tested | \n\t\t|
Miscibility Method A (90% lubricant in fuel) | \n\t\t\tEN228 | \n\t\t\tGood | \n\t\t\tGood | \n\t\t\tGood | \n\t\t\tGood | \n\t\t\tnot tested | \n\t\t
E85 | \n\t\t\tPoor | \n\t\t\tPoor | \n\t\t\tGood | \n\t\t\tGood | \n\t\t\tGood | \n\t\t|
Miscibility Method B (2% lubricant in fuel) | \n\t\t\tEN228 | \n\t\t\tGood | \n\t\t\tGood | \n\t\t\tGood | \n\t\t\tGood | \n\t\t\tGood | \n\t\t
E85 | \n\t\t\tPoor | \n\t\t\tPoor | \n\t\t\tPoor | \n\t\t\tPoor | \n\t\t\tGood | \n\t\t
Properties of the engine oils
*Rating on base 10
Wettability of the surface of the cylinder liner by lubricating oil is important for corrosion- and wear-protection of the piston rings and cylinder liner at the start-up when the temperature of the components is low. In this work, the wetting characteristic of the tested oils was determined using the Sessile Drop method. The resulting contact angles of the drops of various oils on the honed surface of the cylinder liner are shown in Table 2. Same method could not be used to determine wettability of the piston ring because of the small width of the ring. Therefore, the following procedure for qualitative comparison of the wettability of the piston ring by different oils in [12] was applied: 1 µl of oil was placed on the circular flat surface of the phosphate cast iron piston ring and then, after 30 s, the extension of the oil drop along this surface was measured.
\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t
SEMO 4 | \n\t\t\t46.1±3.1 | \n\t\t\t5.33±0.04 | \n\t\t
SEMO 5 | \n\t\t\t43.4±0.2 | \n\t\t\t5.39±0.05 | \n\t\t
SEMO 10 | \n\t\t\t33.1±1.1 | \n\t\t\t7.01±0.12 | \n\t\t
SEMO 36 | \n\t\t\t50.8±0.5 | \n\t\t\t3.78±0.17 | \n\t\t
Contact angle and oil spread distance
The contact angle for SEMO 36 oil on the honed cast iron was the highest among all the tested lubricating oils. The contact angles of SEMO 5 and SEMO 4 were very similar one to each other and only slightly lower than for SEMO 36. SEMO 10 had the lowest contact angle and the largest drop spread for all tested oils. The behaviour of the drop spread of the tested lubricating oils over the piston ring surface is similar to that of the contact angle, bearing in mind that large contact angle values correspond to small spread distances.
Biodegradability and toxicity of the lubricating oils were examined according to the recommendations of the Organization for Economic Co-operation and Development (OECD) in [5]. Biodegradability of lubricating oils was tested using OECD 301F Manometric Respirometry Method consisting of the measurement of oxygen uptake by a stirred solution of the test substance in a mineral medium, inoculated with micro-organisms in [6]. Toxicity of the lubricating oils was studied using “Alga, Growth Inhibition Test” OECD 201 in [7] and ”Daphnia Magna” 24 h Acute Immobilisation Test OECD 202 in [8]. In the “Alga, Growth Inhibition Test”, selected green algae were exposed to various concentrations of the test oils over several generations under defined conditions. Results of biodegradability test are shown in Table 3. As expected, all synthetic ester base oils successfully passed the biodegradability test, while the reference mineral oil was not biodegradable according to the standard procedure OECD 301 Biodegradation of SEMO 5 and SEMO 10 exceeded 70%. In toxicity tests both with Alga and Daphnia Magna, the oils were classified as not harmful for aquatic organisms according to the standard procedures OECD 201 and 202 (see Table 4).
\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t
7 | \n\t\t\t29.4 | \n\t\t\t41.3 | \n\t\t\t25.2 | \n\t\t\t27.6 | \n\t\t
14 | \n\t\t\t36.2 | \n\t\t\t68.4 | \n\t\t\t53.5 | \n\t\t\t38.7 | \n\t\t
21 | \n\t\t\t52.0 | \n\t\t\t79.6 | \n\t\t\t69.6 | \n\t\t\t33.4 | \n\t\t
28 | \n\t\t\t61.1 | \n\t\t\t81.2 | \n\t\t\t75.7 | \n\t\t\t51.2 | \n\t\t
Ultimate | \n\t\t\t> 60% | \n\t\t\t> 60% | \n\t\t\t> 60% | \n\t\t\t< 60% | \n\t\t
Biodegradability of oils (% of biodegraded oil) in [12].
\n\t\t\t\t\t | \n\t\t\t\t||||
SEMO 4 | \n\t\t\t>100 | \n\t\t\tnot harmful * | \n\t\t\t>1000 | \n\t\t\tnot harmful * | \n\t\t
SEMO 5 | \n\t\t\t>100 | \n\t\t\tnot harmful * | \n\t\t\t>1000 | \n\t\t\tnot harmful * | \n\t\t
SEMO 10 | \n\t\t\t>100 | \n\t\t\tnot harmful * | \n\t\t\t>1000 | \n\t\t\tnot harmful * | \n\t\t
SEMO 36 | \n\t\t\t- | \n\t\t\t- | \n\t\t\t>1000 | \n\t\t\tnot harmful * | \n\t\t
Results of the toxicity tests in [12].
*With respect to aquatic organisms.
EC50/EL50 is that concentration of test substance which results in a 50% reduction in either growth or growth rate relative to the control.
Tribological evaluation of lubricating oils was done using ball-on-disk configuration with reciprocating motion according to the standard procedure DIN 51834-2 in [9]. Ball and disk were made of 100Cr6 steel. The ball, 10 mm in diameter, performed reciprocating motion with a stroke of 1 mm and a friction frequency 50 Hz. Normal load was 50 N during short run-in period 45 s and 300 N during the test 60 min. The ball and the disk were immersed in the lubricating oil, which temperature during the test was constant and 50 °C. Friction force was measured as function of time. Friction coefficient was calculated as the ratio of the tangential force to the normal force.
After test completion, diameter of the wear scar on the ball was measured using optical microscope, and, from this data, volume wear of the ball was calculated for each lubricating oils tested.
Evolution of the friction coefficient in friction evaluation tests is shown in Figure 1. Oils with low additive content: SEMO 4, SEMO 5 and SEMO 10 showed an interval of frictional instability after the run-in period. In the instability period, which lasted from 400 up to 800 s, there are some sharp peaks indicating damage of surface and seizure, probably due to micro-welding. The reference lubricating oil had a less pronounced instability period without sharp peaks, while SEMO 36 did not present any instability. Final values of friction coefficient after 60 min and the diameters of the wear scar on the ball are shown in Table 5.
Evolution of friction coefficient in time during tribological evaluation tests of the following oils: a) SEMO 4, b) SEMO 5, c) reference oil, d) SEMO 10, e) SEMO 36. Inset in graph e) shows the initial part of the plot together with the curve of the normal load in [
\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t
SEMO 4 | \n\t\t\t0.119 ± 3.40*10-5\n\t\t\t | \n\t\t\t884 | \n\t\t\t6.01*10-3\n\t\t\t | \n\t\t
SEMO 5 | \n\t\t\t0.111 ± 4.34*10-5\n\t\t\t | \n\t\t\t885 | \n\t\t\t6.02*10-3\n\t\t\t | \n\t\t
REF | \n\t\t\t0.122 ± 2.73*10-5\n\t\t\t | \n\t\t\t517 | \n\t\t\t6.99*10-4\n\t\t\t | \n\t\t
SEMO 10 | \n\t\t\t0.125 ± 3.81*10-5\n\t\t\t | \n\t\t\t929 | \n\t\t\t7.32*10-3\n\t\t\t | \n\t\t
SEMO 36 | \n\t\t\t0.123 ± 1.54*10-5\n\t\t\t | \n\t\t\t459 | \n\t\t\t4.36*10-4\n\t\t\t | \n\t\t
Friction coefficient and wear of the ball in tribological evaluation test of oils (DIN 51834-2) in [12].
The volume of worn material of the ball was estimated geometrically on the basis of the diameter of the wear scar using the following equation (1):
where
Wear specific energy,
Where
In this study, only ball wear was determined as specified by DIN 51834-2. So, the absolute value of wear specific energy could not be determined; since wear of the disk was not measured. However, by using the ball mass loss in the denominator of eq. (2), the upper bound estimation of the wear specific energy can be determined. This upper bound can be used for qualitative comparison of anti-wear properties of the lubricating oils under constant friction conditions. These values, determined using eq. (2), are shown in Figure 2. SEMO 36 and the reference oil have much higher values of the wear specific energy, than other oils. Therefore, these lubricating oils improve contacting surfaces wear protection since much larger energy should be dissipated to produce the same wear as compared to SEMO 4, SEMO 5 and SEMO 10 lubricants.
Friction coefficient and wear specific energy in [
Tribological simulation was performed using cast iron phosphated piston ring and cast iron cylinder liner using reciprocating motion configuration. The samples for the tests were cut from real engine parts (Minsel M165 two-stroke engine manufactured by Abamotor Energía) keeping original curved surfaces and surface finishing. The conformal contact between the piston ring and the cylinder counterpart was reproduced by placing a piston ring on a suitable frame, A, and fixing it by means of a clamp, B (Figure 3). Wear of the components was determined by weighting and geometry measurements.
Experimental set-up for piston ring/cylinder liner simulation.
The piston ring segments performed a reciprocating motion with a stroke of 1 mm and a friction frequency 40 Hz. Normal load was 50 N during short run-in period 45 s and 300 N during the test 90 min. During the test, the piston ring segment and the cylinder liner sample were immersed in the oil, which temperature was constant at 200 °C.
The mass change of the piston ring segments and cylinder liner sample was determined from weighting the components before and after friction tests. Since the mass change can be due to two competitive processes: (i) wear out and (ii) deposit formation from the oil at elevated temperature, estimation of wear out by weighting can give erroneous results. Indeed, after the tests the surface colour became yellowish and remained after dissolvent cleaning indicating some sparingly soluble deposits formed on the surface due to some chemical reaction. Therefore, in addition to the determination of the mass change, worn volume was calculated from surface geometry. Surface morphology of the friction zone was studied using white light confocal microscopy at three different zones along the wear track on the cylinder liner sample. The acquired 3D surface images were 0.5 mm wide in the direction of friction and each image contained 138 cross-section profiles of the wear track yielding totally 414 profiles for each sample. Firstly, the cross-section profiles were averaged for each sample and then among different samples tested using the same lubricating oil. Worn volume of the samples of cylinder liner was calculated as a product of a mean cross-section area of the groove and the total length of the groove. The cross-section area was determined by numerical integration of the cross-section profiles and then worn mass was calculated from the worn volume using the density of cast iron.
Surface chemical composition of the friction zone of cylinder liner samples was characterized using Energy Dispersion X-Ray Spectroscopy (EDS).
Evolution of friction coefficient in time during friction between piston ring segment and a piece of the cylinder liner is shown in Figure 4. It is possible to highlight the increment of the coefficient of friction
Initial friction coefficient was about 0.2 and the final one about 0.33 in both cases. SEMO 10 and SEMO 36 showed different behaviour. The initial values were 0.2 and 0.14 for SEMO 10 and SEMO 36, correspondingly.
Evolution of friction coefficient in time during piston ring/cylinder liner simulation test. a) SEMO 4, b) SEMO 5, c) reference oil, d) SEMO 10, e) SEMO 36. Inset in the graph e) shows the initial part of the plot together with the curve of the normal load in [
At the beginning, after a run-in period, friction coefficient increased and reached maximum. For SEMO 36 the maximum was reached usually between 100 and 200 s from the beginning of the test, while for SEMO 10 the period of increase was longer and the maximum was reached after 700 to 1700 s from the beginning of the test. After reaching the maximum, friction coefficient decreased slowly and stabilized at 0.14 and 0.11 for SEMO 10 and SEMO 36, correspondingly. The friction coefficient of lubricant SEMO 10 showed a slow decline until reaching a constant value lower than the reference one. Friction coefficient for the improved lubricant SEMO 36 levelled out rapidly at a very low value and showed less scatter, probably due to some sort of surface deposition on the contact surfaces.
The averaged cross-section profiles of each liner sample tested are reported in Figure 5. Different scales of magnitude are used for better visualization of the mean contact surface profile. It is possible to notice very good performance of the lubricant SEMO 10 and its improvement in the lubricant SEMO 36. Samples tested using SEMO 4 and SEMO 5 had deep grooves with the maximum depth 22 to 25µm. The samples tested using the reference oil and SEMO 10 had less deep grooves with a maximum depth of 4 to 5µm. Surface of the samples tested using SEMO 36 oil had some thin scratches in the direction of friction while grooves had not been formed.
Average cross-section profile of the friction zone of cylinder liner samples tested using different lubricants in [
Figure 6 shows images of the friction zone of the piston ring segments after friction simulation tests with different lubricating oils. Wear and damage of the surface as function of the oil used was similar to that in the cylinder liner. In tests with SEMO 4 and SEMO 5, the material in the friction zone was heavily damaged. The wear can be classified to be of the adhesive type with intensive plastic deformation and edging. When the reference oil and SEMO 10 oil were used in the tests, the damage of the material was less pronounced than for SEMO 4 and SEMO 5, but the wear in all cases was of the adhesive type. Only small damage was observed on the piston ring segments when using SEMO 36. In this case, only summits of the circular grooves of the piston ring presented some wear and deformation. From the point of view of hydrodynamic lubrication these results may seem to be surprising, since, with the same additive composition, higher wear rate occurs for thinner oil (SEMO 10 in our case) than more viscous oils (SEMO 4 and SEMO 5). Therefore, these results lead to the following conclusions: 1) the lubrication regime should be of a boundary type and 2) surface protection against wear for SEMO 10 and SEMO 36 oils seems to be resulting from the formation of surface layer as a result of adsorption of oil components or tribochemical reactions between the oil components and the base material.
Optical images of the friction zone of the piston ring segments after friction simulation tests using different lubricants. The scale of each image is the same and shown by a scale bar in [
Results of the mass change measurements of the components are shown in Table 6. Worn mass calculated from the worn volume is plotted vs. measured mass change in Figure 7 (dots). The experimental data are fitted by linear function with two adjusted parameters: slope and intersect (dashed line in Figure 7). The solid line is a linear fit with a fixed slope 1 and adjusted intersect. Coefficients of determination for these linear regressions are 0.983 and 0.949, correspondingly, indicating statistically significant linear relationship between the mass change and worn mass determined from the geometry of the groove. Therefore, the deposit formation has not much influence on the mass change and the last can be used as a measure of the components wear out in these tests. The upper bound of the wear specific energy was determined in accordance with eq. (2), using the cylinder liner mass change in the denominator of eq. (2).
\n\t\t\t\t | \n\t\t\t\n\t\t\t\t | \n\t\t\t\n\t\t\t\t | \n\t\t\t\n\t\t\t\t | \n\t\t|
\n\t\t\t\t | \n\t\t\t\n\t\t\t\t | \n\t\t|||
SEMO 4 | \n\t\t\t0.34 | \n\t\t\t-3.95 | \n\t\t\t-1.41 | \n\t\t\t-1.12*10-2\n\t\t\t | \n\t\t
SEMO 5 | \n\t\t\t0.32 | \n\t\t\t-3.68 | \n\t\t\t-3.22 | \n\t\t\t-9.8*10-3\n\t\t\t | \n\t\t
REF | \n\t\t\t0.20 | \n\t\t\t-1.1 | \n\t\t\t-0.64 | \n\t\t\t-1.74*10-3\n\t\t\t | \n\t\t
SEMO 10 | \n\t\t\t0.14 | \n\t\t\t-0.94 | \n\t\t\t-1.25 | \n\t\t\t-2.3*10-3\n\t\t\t | \n\t\t
SEMO 36 | \n\t\t\t0.11 | \n\t\t\t-0.09 | \n\t\t\t1.23 | \n\t\t\t0 | \n\t\t
Results of friction simulation tests in [12].
Mass wear determined from the geometry of the groove vs. mass change of the cylinder liner samples. The dashed line is a linear regression of experimental data with two adjusted parameters: slope and intercept. The solid line is a linear regression with a fixed slope 1 in [
Final friction coefficient and wear specific energy are shown in Figure 8. SEMO 36 oil showed the best antifriction and wear resistance characteristics among all tested lubricants. Friction coefficient was almost a half of that for the reference oil, while specific wear energy was 7.8 times higher than for the reference oil. In comparison with the ball-on-disk tests, wear specific energy for SEMO 36 lubricant was much lower in the tribological simulation test; however, oil temperature in these two tests was different. When the ball-on-disk evaluation tests were performed at the same temperature as in the simulation test (200 °C), the value of wear specific energy was similar to that in the simulation test: 0.14 GJ/g in the ball-on-disk at 200 °C vs. 0.18 GJ/g in the piston ring/cylinder liner simulation test. Although these values are only upper bound estimations of the real values, they are close to one another. According to the structural-energetic approach in [10], this means that the dominating wear mechanism in both cases is the same. Then, a significant decrease in the wear specific energy from 3.97 to 0.14 GJ/g with temperature increase from 50 to 200 °C implies changing in dominating wear mechanism at higher temperature. It can be stated that, under the applied experimental conditions, the chemical compositions of the base oil and the additives had greater influence on the tribological performance of the lubricants than their rheological properties.
Friction coefficient and wear specific energy in friction simulation tests in [
Surface chemical composition of the friction zone of cylinder liner samples was characterized using Energy Dispersive X-Ray Spectroscopy (EDS). Table 7 shows surface chemical composition for three different surfaces:
friction zone of the cylinder tested using SEMO 36 lubricant,
untouched surface of the same cylinder, and
reference cylinder not immersed neither heated in lubricating oil.
\n\t\t\t\t | \n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t
Friction zone | \n\t\t\t61.5±1.9 | \n\t\t\t11.5±0.7 | \n\t\t\t23.5±3.2 | \n\t\t\t2.83±0.68 | \n\t\t\t0.615±0.085 | \n\t\t
Untouched zone | \n\t\t\t84.0±3.6 | \n\t\t\t7.36±0.46 | \n\t\t\t3.41±3.31 | \n\t\t\t4.19±0.07 | \n\t\t\t1.11±0.17 | \n\t\t
Reference sample | \n\t\t\t92.5±0.3 | \n\t\t\t2.95±0.46 | \n\t\t\t0.1 | \n\t\t\t3.59±0.52 | \n\t\t\t0.935±0.255 | \n\t\t
Surface chemical composition (at.%) of the cylinder liner samples tested with SEMO 36 lubricating oil
Silicon and manganese were alloying elements of the base material and did not show important variations in their concentration, whereas the most important variation was in the carbon and oxygen content. There was no significant difference for other elements since the oils had no metal-containing additives. Figure 9 shows surface concentration of four elements relative to iron. After the test, during which a cylinder was immersed in the SEMO 36 oil and heated at 200 °C, carbon and oxygen concentrations on untouched surfaces were slightly higher than on the reference sample, e.g., the sample not immersed into the oil. However, carbon and oxygen concentrations drastically increased on the surface of the friction zone, on which carbon was each forth atom. Also, in contrast to the untouched surface and the reference surface, on the surface of the friction zone, carbon concentration was higher, than the oxygen one. One can infer from these data that friction induced tribochemical reactions between oil components and base material to form surface layer enriched with carbon and oxygen. This surface layer or sliding lacquer may protect mating surfaces from adhesion and/or damage yielding lower friction and wear in [10].
Surface concentration of elements relative to iron in [
After previous simulation tribological test the performance of the oils was evaluated in real two-stroke engines (Minsel M165) with a swept volume of 158 cm³, a stroke of 54 mm, compression ratio 7,1:1, power (ISO 1585) 3.53/4.8 kW/HP, maximum torque 120 Nm and 4500 rpm rotation speed. Scuffing tests were performed using various lubricating oil – petrol mixtures in order to evaluate the lubricating performance of the lubricants under extreme load conditions. The test conditions applied are shown in Table 8, and the tested oil-fuel compositions are shown in Table 9.
Figure 10 shows the photographs of the engine components after scuffing tests, in which the reference mineral oil was used in a mixture with pure petrol and bioethanol. Increase in the bioethanol content in the fuel led to decrease in carbon soot deposition on the engine cylinder and piston. Also, when bioethanol was used, the surface was less damaged under extreme working conditions.
\n\t\t\t\t | \n\t\t\t\n\t\t\t\t | \n\t\t\t\n\t\t\t\t | \n\t\t\t\n\t\t\t\t | \n\t\t|
\n\t\t\t\t | \n\t\t\t\n\t\t\t\t | \n\t\t|||
1 | \n\t\t\t2000 | \n\t\t\t5 | \n\t\t\t0 | \n\t\t\t0 | \n\t\t
2 | \n\t\t\t4000 | \n\t\t\t20 | \n\t\t\t50 | \n\t\t\t2.4 | \n\t\t
3 | \n\t\t\t4000 | \n\t\t\t20 | \n\t\t\t75 | \n\t\t\t3.2 | \n\t\t
4 | \n\t\t\t2000 | \n\t\t\t5 | \n\t\t\t0 | \n\t\t\t0 | \n\t\t
5 | \n\t\t\t4500 | \n\t\t\t90 | \n\t\t\t100 | \n\t\t\tfull load | \n\t\t
6 | \n\t\t\t2000 | \n\t\t\t5 | \n\t\t\t0 | \n\t\t\t0 | \n\t\t
Experimental conditions for scuffing tests of real two-stroke engines
\n\t\t\t\t | \n\t\t\t\n\t\t\t\t | \n\t\t\t\n\t\t\t\t | \n\t\t|
\n\t\t\t\t | \n\t\t\t\n\t\t\t\t | \n\t\t||
Petrol | \n\t\t\t2% | \n\t\t\t2% | \n\t\t\t2% | \n\t\t
E10 | \n\t\t\t2% | \n\t\t\t- | \n\t\t\t- | \n\t\t
E20 | \n\t\t\t2% | \n\t\t\t- | \n\t\t\t- | \n\t\t
E85 | \n\t\t\t2% | \n\t\t\t- | \n\t\t\t2% | \n\t\t
Oil – petrol combinations tested in a real two-stroke engine scuffing test
Macro images of two-stroke engine components after scuffing test using a mixture of mineral oil with petrol (a,d), bioethanol E10 (b,e) and bioethanol E20 (c,f) in [
Macro images of two-stroke engine components after scuffing test using mixture of SEMO 10 lubricating oil with petrol: a) piston, b) cylinder, c) exhaust side, d) intake in [
Figures 11 show the photographs of the engine components after scuffing tests using a SEMO 10 – petrol mixture. Some seizure between compression piston ring and cylinder was observed when using a mixture of SEMO 10 with petrol. Several vertical abrasion marks were formed in the exhaust zone of the cylinder, where the temperature was higher. However, the piston and cylinder were quite clean with only some carbon soot deposits in the exhaust zone. The state of the cylinder head was quite healthy and clean in the intake zone, the carbon residues were considered normal.
Figure 12 shows the pictures of the engine components after scuffing test using SEMO 36 lubricating oil with petrol and bioethanol fuels. When using a mixture of SEMO 36 with bioethanol E85 or petrol, no scuffing or seizure was observed. Only light scratches were found on the cylinder surface, which were more pronounced when using petrol. In this case, carbon soot deposits formed intensively on the top part of the piston. The piston and cylinder were very clean, when using bioethanol.
Macro images of two-stroke engine components after scuffing test using mixture of SEMO 36 lubricating oil with bioethanol E85 (a, b, c) and petrol (d, e, f): a), b), d), e) piston, c), f) cylinder in [
In addition, gaseous emissions from the engine were analyzed for various fuel-oil mixtures with different proportions of bioethanol to petrol: 20%, 30% and 85%. The gas emissions were measured using the Directive CE 2002/88, Portable, SH3 modality as reference limits. The differences in power and consumption were negligible when using bioethanol E10 and E20. When compared with the petrol, the NOx emissions showed an increasing trend and the emissions of CO and CH diminished in tests with bioethanol and reference oil. When using E85, the reference mineral oil was not miscible, but the new developed oil SEMO 36 was totally miscible. When using bioethanol E85, a considerable reduction in engine power was observed yielding value 13% to 22% less than in the tests with petrol. At the same time fuel consumption increased slightly between 7% and 20%, and gaseous emissions were considerably reduced (see Table 10). When using SEMO 36 the reduction in NOx emission was the most significant as compared with other gases and was probably due to the lower temperature generated.
\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t \n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t \n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t
SH3 Limit Normative | \n\t\t\t\n\t\t\t | \n\t\t\t | 5.36 | \n\t\t\t161 | \n\t\t\t603 | \n\t\t
Petrol/Ref. Oil 2% | \n\t\t\t5.46 | \n\t\t\t397 | \n\t\t\t1.469 | \n\t\t\t139.8 | \n\t\t\t333.2 | \n\t\t
E10 + 2% Ref. oil | \n\t\t\t5.44 | \n\t\t\t385 | \n\t\t\t1.573 | \n\t\t\t124.1 | \n\t\t\t314.8 | \n\t\t
E20 + 2% Ref. oil | \n\t\t\t5.5 | \n\t\t\t382 | \n\t\t\t2.29 | \n\t\t\t128 | \n\t\t\t251.5 | \n\t\t
E85 + 2% Ref. oil (not miscible) | \n\t\t\t4.8 | \n\t\t\t427 | \n\t\t\t2.29 | \n\t\t\t109.8 | \n\t\t\t43.11 | \n\t\t
E85 + 2% SEMO 36 (miscible) | \n\t\t\t4.3 | \n\t\t\t478 | \n\t\t\t0.689 | \n\t\t\t119.5 | \n\t\t\t32.93 | \n\t\t
Emission of gases from two-stroke engine tested with different lubricating oil– petrol combinations in [12].
The lifecycle analysis for a 2-stroke engine fed by petrol and E85 was carried out using the model M 165 Minsel engine running in a tiller during 1000 h, which characteristics are shown in Table 11.
Model of machine | \n\t\t\tTiller 3002 | \n\t\t
Machine weight | \n\t\t\t90-110 kg | \n\t\t
Engine model | \n\t\t\tM165 Minsel 2-stroke | \n\t\t
Engine weight | \n\t\t\t12.8 kg | \n\t\t
Engine life | \n\t\t\t1000 h | \n\t\t
Scuffing test results | \n\t\t\tOK | \n\t\t
Engine power | \n\t\t\t3 kW | \n\t\t
Emissions | \n\t\t\tDirective 97/68/CE and later 2002/88/CE and 2004/26/CE | \n\t\t
Characteristics of the engine used in life-cycle analysis
Two fuel + oil pairs named as “Cleanengine systems” were compared with the Conventional system for the same engine working in the same application. In the alternative Cleanengine system I the engine was fed by a mixture of bioethanol E20 and mineral oil. In the alternative Cleanengine system II, the engine was fed by bioethanol and newly developed advanced and biodegradable lubricating oil SEMO 36. The fuel and oil consumption for the conventional and two alternative systems is shown in Table 12.
\n\t\t\t\t | \n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t
Fuel consumption per functional unit | \n\t\t\tPetrol 900 kg | \n\t\t\tBioE20 1123 kg | \n\t\t\tBioE85 1405 kg | \n\t\t
Oil consumption per functional unit | \n\t\t\tMineral oil 36 kg | \n\t\t\tMineral oil 23 kg | \n\t\t\tSEMO 36 29 kg | \n\t\t
Parameters of the conventional and alternative systems used in the life-cycle analysis
The Eco-indicator 99 Methodology was used for the Impact Assessment method. The components of the environmental impact are shown in Figure 13 a), while the total environmental impact is shown in Figure 13 b). Almost all components of the environmental impact as well as the total environmental impact were higher for fossil fuel. However, the climate change was more affected by the renewable system.
Results of the life-cycle and environmental impact analysis for the conventional and two alternative systems: a) components of the environment impact, b) total environmental impact in [
The global environmental impact evaluated by Lifecycle Assessment tools for the Cleanengine system I and II using bioethanol was lower than for the reference system using petrol. The comparison between two alternative systems Cleanengine I and Cleanengine II showed that the last one had slightly higher environmental impact due to higher fuel and lubricant consumption that can be related to the lower calorific value of the ethanol compared to the petrol. While the reduction of the environmental impact is attributed to the reduction in emissions, the use of a biodegradable nontoxic lubricant will further reduce the environmental impact of the Cleanengine II system.
Compared to conventional liquid hydrocarbon fuels, bio-fuels exhibit considerable differences in their physical properties which significantly influence on the injector flow as well as on primary and secondary spray break-up processes. As a consequence, spray mixture formation of bio-fuels is considered to be largely different compared to conventional fuels under engine operating conditions with severe consequences on the combustion and emission characteristics. Hence, injection and combustion system optimization as well as optimization of the injector configuration (number of nozzle holes, diameter, spray targeting, etc.) for bio-fuels requires a detailed knowledge of how the fuel properties influence the injector flow and spray atomization characteristics. Optimization of the nozzles materials and design is an important task which will open new markets and enlarge the number of potential customers for eco-friendly applications.
Different metal-doped DLC coatings were developed by Physical Vapour Deposition method (PVD). Friction and wear tests were carried out using SRV tribometer with “cylinder-on-disc” configuration in lubricated conditions. The coatings were deposited on steel cylinders and disks. The cylinder, 15 mm in diameter, performed reciprocating motion with a stroke of 2 mm and a friction frequency 50 Hz. Normal load was 50 N during short run-in period 30 s and 200 N during the test 60 min. The cylinder and the disk were immersed in fluids, which temperature during the test was constant and 25 °C.
Both Cr- and Ti DLC coatings had good friction and wear behaviour and they could be a good alternative to improve tribological properties of the actual uncoated nozzles.
Average cross-section profile of the friction zone of discs samples (uncoated reference, Cr and Ti DLC) tested using different fuels, AGIP and B50. Different scales of magnitude are used for better visualization of the mean contact surface profile.
Surface morphology of the friction zone was studied using white light confocal microscopy. The averaged cross-section profiles for each sample tested are shown in Figure 14. It is possible to notice very good performance of the coatings, them had deeper grooves with a maximum depth of 5.45 µm. Cr DLC tested against AGIP fuel had better performance than Ti DLC. Two different scales of magnitude, Z, are used for better visualization of the mean contact surface profile. From 5 to -5µm for coated discs (Cr DLC and Ti DLC lubricated with AGIP ref and B50) and from 16 to -16µm for uncoated ref samples.
Corrosion resistance of different materials and coatings used for nozzles fabrication (Cr and Ti DLC) was characterized using electrochemical impedance spectroscopy and potentiodynamic polarization techniques in order to determine the kinetics parameters and the corrosion mechanisms of these materials in NaCl 0.5M or K2SO4 0.2M in [12].
Base nozzles material, uncoated steel X82WMo, was also characterized under corrosion conditions and compared with DLC coated samples of the same material. The electrolyte used in these tests was K2SO4 0.2M. Cr DLC coating offered excellent corrosion protection. The coating did not exhibit any pores or defects, protecting effectively the substrate during immersion.
Open-circuit potential (OCP) was measured during 2200 s in order to analyze the samples tendency with the exposure time. After that, an electrochemical impedance spectroscopy was performed in a frequencies range from 10 k to 10 mHz. Once impedance measurements finished, a potentiodynamic potential swept was applied from OCP-0.2 V to OCP+0.6 V at a scan rate of 0.5 mV/s.
Coated nozzles had more positive potential than the reference ones. For all surfaces, OCP was stable after first 2200 s of immersion. The difference between three nozzles regarding impedance results was very notable. Cr and Ti DLC coated samples had a semicircle Nyquist diagrams implying that the electrolyte did not reach the substrate during the immersion in the dissolution. The coating acted as an effective protective barrier. Uncoated nozzle had lower corrosion resistance. Two time constants could be clearly distinguished from two maxima in the Nyquist plots.
Nyquist diagrams. Impedance data of coated and uncoated nozzle in K2SO4.
Table 13 shows the parameters obtained from equivalent circuit simulation of the experimental data and Figure 16 shows the equivalent circuits used in the simulation process.
\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t
Nozzle Uncoated | \n\t\t\t-0.556 | \n\t\t\t0.035 | \n\t\t\tYo=58.45 n=0.82 | \n\t\t\t1.10 | \n\t\t\tYo=140.7 n=0.94 | \n\t\t\t\n\t\t |
Nozzle Cr DLC | \n\t\t\t-0.022 | \n\t\t\t12780 | \n\t\t\tYo=0.75 n=0.94 | \n\t\t\t- | \n\t\t\t- | \n\t\t\t- | \n\t\t
Nozzle Ti-DLC | \n\t\t\t-0.354 | \n\t\t\t10.38 | \n\t\t\tYo=0.34 n=0.639 | \n\t\t\t- | \n\t\t\t- | \n\t\t\tYo=0.02 B=3.23 | \n\t\t
Equivalent circuit parameters of coated and uncoated nozzles
Equivalent circuits used for the experimental data simulation. Circuit A) for Nozzle Cr DLC; circuit B) for uncoated nozzle and circuit C) for Ti DLC coating.
Polarization curves for the coated nozzle are shown in Figure 17.
Polarization curves on coated and uncoated nozzles immersed in K2SO4
Cr DLC coating had passive behaviour and low corrosion current of the order of 10-9A for potentials near to OCP. Coating Ti DLC also had passive behaviour in a wide zone of the anodic branch. Cr DLC and Ti DLC notably improved substrate corrosion behaviour reducing its corrosion current by several orders of magnitude (see table 14).
\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t\t\n\t\t\t\t\t | \n\t\t\t
Nozzle Ref. Uncoated | \n\t\t\t-0.533 | \n\t\t\t18.5 | \n\t\t
Nozzle Cr DLC | \n\t\t\t-0.039 | \n\t\t\t0.003 | \n\t\t
Nozzle Ti DLC | \n\t\t\t-0.331 | \n\t\t\t0.18 | \n\t\t
Corrosion current of coated and uncoated nozzles calculated using Tafel approach
The injectors were tested in the Minsel M-430 engine manufactured by Abamotor Energía, SL. The parameters of the engine and test conditions are shown in Table 15.
Bore | \n\t\t\t85 mm | \n\t\t
Stroke | \n\t\t\t75 mm | \n\t\t
Displacement | \n\t\t\t426 c.c. | \n\t\t
Compresion ratio | \n\t\t\t19,3: 1 | \n\t\t
Power NB | \n\t\t\t8,4 / 8,7 Cv | \n\t\t
Rpm | \n\t\t\t3000 | \n\t\t
Torque | \n\t\t\t23Nm / 2000 RPM | \n\t\t
Dry weight | \n\t\t\t45 Kg | \n\t\t
Characteristics of the engine used in engine tests to evaluate the different alternative nozzles (Cr DLC and Ti DLC).
During the test the engine worked for 50 hours at full load (3000 rpm). Biodiesel B30 was used as a fuel, which was a mixture of FAME (100% Biodiesel) with diesel B at a rate of 30%.
The engine on test bench and the tested nozzles installed on the engine
Scanning electron microscope (SEM) and energy dispersion X-Ray spectroscopy (EDS) were used for characterization of the nozzles geometry after the engine tests. Cr DLC coating had better behaviour than Ti DLC.
The microanalysis showed that for the all coatings the deposited layer on the needle persisted after the test, with the exception of the tip where the Ti DLC layer has been detached
Additionally, the spray holes geometries of the nozzle body were analysed after endurance test with two different fluids: reference standard fuel and 30% biodiesel.
Figure 19 shows the scanning electron microscope images (EDS) of the nozzle body tip before the engine test (real part and its corresponding silicon model for orifices internal characteristics analysis), whereas Figures 20 and 21 show the nozzles after the tests with standard diesel fuel and B30 fuel, correspondingly. Though large quantities of carbonaceous deposits could be observed on free surfaces for both fuels, no deposits were found on internal surface of spray holes.
Nozzle body tip and silicon model with labelled holes
Images of the nozzle after endurance test with standard diesel fuel
Images of the nozzle after endurance test with B30 fuel
Finally, nozzle deposits were analyzed by Thermal Gravimetric Analysis (TGA), which showed no big difference in deposits composition for the nozzles operated with standard diesel and B30 blend.
Fully formulated prototype lubricants based on synthetic esters had low toxicity for aqueous organisms (algae and Daphnia Magna) and high biodegradability evaluated by the Manometric Respirometry Method.
Among three developed prototype lubricating oils, SEMO 10 had the best tribological performance which was comparable with that of the reference mineral oil. Further improvement of the tribological properties of this lubricating oil was achieved by additive re-formulation. The developed lubricant, SEMO 36, exceeded the reference mineral oil in tribological performance.
Our findings indicated that, in addition to the rheological properties of the lubricating oil, deposit build-up was an important factor controlling the tribological performance of the oil both in simulation experiments and real two-stroke engines. Two kinds of deposits: carbon soot and transparent sliding lacquer were observed on the engine components after tests. Build-up of a transparent sliding lacquer was especially important in the case of SEMO 36 oil and it was related with considerable reduction both in wear rate and friction coefficient. For SEMO 36, surface chemical analysis of the friction zone showed important changes in surface chemical composition, which was especially marked by increase in carbon and oxygen content. It is evident that formation of the sliding deposits stemmed from tribochemical reactions between the oil components and base material (cast iron and steel). The chemical state of carbon and oxygen atoms on the surface of friction zone should be further investigated for better understanding of these mechanisms.
Tests in real two-stroke engines were performed using mixtures of the developed lubricant with petrol or bioethanol. In both cases, no seizure between piston ring and cylinder liner was observed. When using bioethanol, the engine components were clean without important carbon soot deposits.
Engine power slightly decreased and fuel consumption slightly increased - on a volumetric basis when bioethanol E85 was blended with the newly developed lubricating oil SEMO 36. However, these results might be related with lower calorific value of ethanol as compared with petrol. Besides, the new lubricating oil improved scuffing resistance in combination with miscible lubricants and significantly reduced the environmental impact. In addition to low toxicity and high biodegradability, emissions of CO, NOx and hydrocarbons from engines lubricated with the newly developed lubricants were lower than with traditional mineral oil and much below the limits established for portable applications.
Concluding, a new generation of lubricating oils for two-stroke engines have been developed combining low friction, good protection against wear and scuffing, no ash residue, low carbon soot or other deposit formation. These lubricating oils are compatible with bioethanol E85.
Application of Cr DLC coating on injection nozzles significantly increased the corrosion resistance and improved behaviour in engine test.
Though Ti-DLC coating also improved substrate corrosion resistance, its performance in engine test was worse than for Cr DLC coating.
Deposit chemical composition and the nozzle performance did not significantly vary in endurance tests when standard diesel was substituted by B30 blend.
The authors acknowledge financial support of the European Commission, the project CleanEngine “Advanced technologies for highly efficient Clean Engines working with alternative fuels and lubes” under contract TST5-CT2006-031241, and the Spanish Minister of Science and Innovation, for co-financing the project under contracts ENE 2008-00652-E/ALT “Tecnologías Avanzadas para motores limpios altamente eficientes, trabajando con combustibles y lubricantes renovables”, RYC-2009-0412 and BIA2011-25653. Also, the authors acknowledge support received from other partners who participated in the projects: ARIZONA Chemical, OBR, GUASCOR Power, BAM, AVL and INSTITUTO MOTORI.
We appreciate the useful help of Olatz Areitioaurtena and Raquel Bayón on performing Biodegradability, toxicity and corrosion characterizations and tests.
The larch species are a typical light-demanding deciduous conifer, ectomycorrhizal (ECM) tree species, and dominant in the northern hemisphere [1, 2]. Among genus
Some larch species are typical afforestation species in NE China, Russian Far East, Korea, and Japan. Most larches can tolerate cold and late frost [8], thus attaining significant biomass with a high growth rate in cold regions [2, 3]. Due to these good growth traits, larch (Japanese larch:
The physical environment surrounding the biosphere has been dramatically changing worldwide. Especially, atmospheric CO2 concentration ([CO2]), nitrogen (N) deposition, and ground-level atmospheric ozone concentration (O3) have increased rapidly since the Industrial Revolution [10, 11]. Furthermore, these physical environmental changes will become serious in the near future because of increased energy demands due to rapid economic growth, industrialization, and urbanization in Asian countries. For sustainable use and adequate management of forest resources, we must therefore clarify the response of trees to these environmental changes.
Nowadays, larch trees are intensively planted and lumbered not only in northern Japan [12, 13] but more widely in the northern Eurasian continent. However, knowledge about the susceptibility of this species to environmental stresses is still limited, except for biological stresses, for example, shoot blight and root rot disease [14], and physical stresses, that is, low temperature [8]. Will larches maintain their high growth rate and extensive establishment under the changing environment? Recently, several researchers have studied effects of environmental changes on larch species [2, 4, 13, 15]. The information will be useful for sustainable use and adequate management of larch plantations. In this chapter, we integrate previous studies examining the growth and ecophysiological responses of larch species including their hybrid to environmental changes, and propose the future direction for utilization of larch species.
Genus
Distribution of larch species in Eurasian continent and Far East Asia (illustrated from: Abaimov et al. [
Other variety of Dahurian larch (
In central Europe, European larch (
Deciduous needle habit of larch species may contribute to the dominance of these species in permafrost regions as compared with an evergreen conifer (
Seasonal change in the water relation in American larch and Black spruce (left), schema of winter desiccation mechanism (right) [
The photosynthetic rate of larches is markedly higher than that of other conifers [25]. However, the initial slope of the light-photosynthetic curve for larch is gentler than that for several conifers, and has similar traits to the C4 plant [26]. The possibility that the larch is a kind of C4 plant was nevertheless disproven by a photosynthesis experiment using 14C-labeled CO2 [26]; larch is concluded as a C3 type plant.
This high growth results from its high photosynthetic rate and unique arrangement of two different types of needles, that is, short-shoot and long-shoot needles [27]. To reveal the photosynthetic characteristics of short- and long-shoot needles of the sunny canopy of the larch trees
Variation of light-saturated photosynthetic rate (Psat) at ambient (left) in short- and long-shoot needles at larch canopy and no variation of Pmax at CO2 saturation (right) located at larch canopy in terms of N content, measured during 2001–2003
The large annual and seasonal variations in Psat in both shoots were found to be mainly determined by climatic variations, while shoot types determined the strategy of their photosynthetic N utilization (N use efficiency, retranslocation, etc.) as well as the stomatal regulation as found in deciduous broadleaved tree saplings grown under larch forest [28].
Although there is no difference in the growth and development of seedlings of Japanese and hybrid larch F1, the temperature dependence of photosynthesis in hybrid larch shows greater photosynthetic starch accumulation capacity than in Japanese larch [29].
Carbon (C) allocation pattern of photosynthates may be essential for the growth and survival of plants [30]. Allocation of photosynthates to the root system in larch seedlings, for instance, can maintain growth at low soil pH [31]. Symbiotic microorganisms in larch root require 10–20% of photosynthates of host plants [32]. Larch seedings inoculated with commercial ectomycorrhiza: ECM (
Assimilation and intercellular CO2 concentration (A-Ci) relation in hybrid larch F1 inoculated with ECM (one species vs. multi-infection) and stomatal limitation (Ls %). Right: A: control; no infection of ECM, B: in infected with commercial ECM (
In fact, the growth of larch species is closely connected with the ubiquitous ectomycorrhizal fungal association. Symbiotic ECM improves nutrients (phosphorus, P; nitrogen, N) and water uptake, and buffers against environmental stress [34, 35, 36, 37, 38].
Photosynthate allocation is essential not only for plant growth and survival but is also directly related to the photosynthetic productivity of forested stands. Photosynthetic production is a compromise between the instantaneous photosynthetic capacity of leaves and leaf longevity (e.g., [22, 34]). Photosynthetic production (biomass) is therefore tightly linked to leaf area index (LAI; leaf area per unit area; m2 m−2). As a result, LAI has been studied in several terrestrial ecosystems. Larch forests have a relatively small LAI value of 4.1 [39] (Table 1). The aboveground production rate of larch in early autumn is estimated to be similar to that of evergreen conifers (e.g.,
Forest type | Foliage mass (ton hm−2) | Leaf area index (LAI) (m m−2) | No. stands | References |
---|---|---|---|---|
Deciduous forests | 2.9 ± 1.5 | 3.0–6.0 | 98 | [40, 41] |
Larch stand | 2.9 ± 1.0 | 2.5–4.5 | 28 | [41, 42] |
Pine (red and black) | 6.8 ± 1.8 | 3.5–6.0 | 60 | [41, 42] |
Evergreen forest | 8.6 ± 2.6 | 5.5–9.0 | 46 | [41, 43, 44] |
Evergreen conifers | 16.0 ± 4.5 | 5.0–10.0 | 49 | [40, 42] |
19.4 ± 4.9 | 4.5–8.5 | 97 | [42, 43] |
Forest types, foliage mass, and LAI.
As summarized by Osawa et al. [2], carbon (C)-allocation of permafrost ecosystem has unique characteristics and key of survival of larch on permafrost in Central and Far East Russia where a vast area of forest exists on continuous permafrost [45]. According to them, “Deciduous coniferous taiga, larch ecosystem is one of the unique biomes in northeastern Eurasian Continent, where a vast area of forest exists on continuous permafrost.” We defined the active soil layer as the melted soil layer between the ground surface to the front of frozen soil. Based on the field survey, three representative sites were selected: (1) a forest near Yakutsk in Yakutian Basin, eastern Siberia (62 N–129E), (2) a forest near Tura in central Siberian Plateau (64 N–100E), and (3) a forest tundra transition near Chersky in Kolyma lowland (69 N–160E) [45]. C storage in these ecosystems was estimated in both aboveground and belowground biomass, in the forest floor, and in active layer as for soil organic C and as carbonate-carbon (Figure 5).
Carbon storage and allocation in different larch ecosystems in eastern Eurasia (Adaptation from: Matsuura et al. [
Matsuura et al. [45] well summarized that organic C in the soil in active layer was the largest component in the sites. Soils in Russia (Yakutsk and Tura) sites indicated carbonate-C accumulation in the active layer, which might result from an extreme continental climate with low annual precipitation of around 200–500 mm year−1 and big temperature range C storage in above- and below-ground biomass varied among sites, however, ratios of above−/below-ground biomass C had a narrow range from 1.1 to 1.5. The high allocation rate of C to below-ground part resulted from a kind of adaptation to effective water and nutrient acquisition under nutrient-limited environment due to low soil temperature for litter decomposition [46].
In this section, we should point out important evidence; “Permafrost layer nurtures light-Taiga and the canopy protects permafrost” [2], especially at Yakutia; northern Far East (FE) Russia. According to the classic idea of climatologists and community ecologists [6, 7], Yakutian vegetation should be steppe or grassland, however, light Taiga mainly composed of larch is well developed [47]. Even under the low precipitation of continental climate, the permafrost provides water from belowground to aboveground, which is accelerated by extra-harvesting, forest fires, global warming [2, 48], etc. However, the accumulation of salt (mainly of Natrium compounds) on the ground surface will inhibit forest regeneration [49]. Much worse, the emission of greenhouse gas (CO2, CH4, N2O, etc.) and unknown microbes will increase from melted permafrost. As an old saying of Yakutian people, “we can make one grave per one.” Alas (=pond appeared after harvest or fire in the Taiga)”, which points to their method of sustainable forest management method (Figure 6).
The Alas developed after harvesting by local people of Yakutia (Adopted from: Koike [
Regeneration of larch is moderate and larch-dominated Taiga is recovered (canopy closure) 20 years after forest fires. This is attributed to an increase in depth of the active soil layer by heat from fires and/or charcoal accumulation. Another 80–100 years and more after the canopy closure, the closed canopy gradually becomes sparse because sunlight to the forest floor is intercepted and will recover the depth of the active soil layer. As a result, competition of aboveground may be caused by limited amount of water and nutrients, but not only by light resources [2, 48].
In China, there are two sections in genus
Section | Species | Elevation (m) | District, location habitat | |
---|---|---|---|---|
Sect. | 300–2800 | Hebei, Heilongjiang, Northwestern Henan, Jilin, Nei Mongol, Shanxi (Daxing’anling, Xiaoxing’anling Mt.) | Rocky slopes, peatlands, swamps, lowland subarctic plains, river basins, valleys | |
( | 600–2800 | Hebei, Northwestern Henan, Shanxi | Usually on rocky slopes | |
500–1800 | Jilin, Eastern Liaoning | Mountains, moist slopes, swamps | ||
500–3500 | Xinjiang, Altai M., Eastern Tianshan M., lowland taiga | Cold, relatively dry, long day-time during July to August | ||
Hebei, Heilongjiang, Henan, Jiangxi, Jilin, Liaoning, Shandong | Introduced, cultivated | |||
Jiangxi (Lu Shan), Liaoning | Introduced, cultivated | |||
Sect. | 3000–4100 | Southern and Eastern Xizang | Mountains | |
2600–4000 | Southeastern Xizang, Northwestern Yunnan | Mountains | ||
3200–3500 | Southeastern Xizang (Gongbo’gyamda) | Rocky slopes | ||
2300–3500 | Sichuan | Mountains | ||
3000–3500 | Southern Xizang | River basins, valleys | ||
2500–4300 (−4600) | Southern Gansu, Southern Shaanxi, Sichuan, SE Xizang, Northern Yunnan | Mountains, river basins |
Distribution of Dahurian larch (
It is the main wood production base in China and one of the main tree species for forest management, and artificial afforestation in Northeast China. With the thawing and shrinking of permafrost, the distribution of
Japanese larch (
Forests in Russian are mainly regulated by forest fires and are naturally regenerated [13, 16, 47]. The Chinese government has been intensively planting three species including larch from 1999 [9, 56]. In Japan, the establishment of plantations of Japanese larch was not successful due to several biological stresses, especially in Hokkaido island [13, 15].
Larch forest conservation and silviculture in Far East Asia should be considered on the high pressure of forest fires [2, 3, 46, 57]. Forest fires have been regulating vegetation dynamics there, especially Russian Far East [47, 57]; the essential role of biochar is well evaluated (Figure 8) [58, 59].
A view of burned larch forest after trunk fire at around Amur state, Russia (Photo courtesy by: Dr. Semyon Bryanin and Dr. Makoto Kobayashi).
Larch (
Larch is naturally distributed in mountain areas of NE China, Inner Mongolia, North China, and SW China. Due to its characteristics of cold resistance, fast growth, fine wood structure, and strong corrosion-resistance, it has become the main afforestation and fast-growing high-yield tree species in northern China [9]. Since the founding of the People’s Republic of China, a large area of larch plantation has been built successively, which is an important reserve forest resource in China [60]. Larch usually forms a large area of the pure forest after forest fires [15, 46, 47, 57], or composition of larch-based mixed forest with birch, poplar, spruce, and other coniferous and broad-leaved trees [46].
According to the data of the 9th National Forest Inventory in China (2014–2018), the national forest coverage rate is 22.96%, with a forest area of 220 million hm2, including 79.54 million hm2 of the artificial forest, ranking first in the world [60]. According to the report of Global Forest Resources Assessment (FRA) in China, the growing stock in the forest of larch species reached about 1,200 million m3 [56]. As dominant tree species components, the top three tree species are oak (
As mentioned above, the Chinese government has been intensively planting three kinds of tree species (Dahurian larch for NE, Chinese fir for SW, and poplar for all parts) on farmlands and degraded areas. This project is called as NFCP, which emphasizes “expansion of natural forests and increasing the productivity of forest plantations” [9], and attained the largest new plantation area in the world [56, 60]. This area by 2019 is larger than the whole Japanese land area. On the occasion of the announcement of the leader Mr. Xi Jinping, one of the Chinese ecological policies orients us on how to conserve forest as an ecological unit. Based on this statement, the conservation of the forest ecosystem is one of the national key projects for “ecological culture city” [61]. However, NFCP proposed they would not harvest their own trees. In connection with this, Chinese trade in timber may strongly depend on forests in Amur state, Russia, and other states located in the opposite bank where no “border” between the two states due to the river frozen during winter.
In Japan, the establishment of larch plantations had been not successful due to several biological stresses, in Hokkaido island as well as a central part of Japan [39]. From silviculture records [53, 62], larch plantation started to use mountain stock in Nagano prefecture in central Japan during 1624–1645. At around 1890, the production method of larch seedlings has established in central Japan and had expanded to Hokkaido around 1910 [18, 53]. Intensive plantation of larch was intended to produce mine timber equipped with high compressive strength by short term rotation culture of around less than 30-year-old.
At the latter 1970’s days, the outbreak of grazing damages on the needle by larch sawfly (
Yearly trend of larch sawfly in Hokkaido Island (after Fujita et al. [
Effects of insect defoliation were studied on the formation of secondary cell walls of tracheids in
Collection of larch seed, representing larch over the whole range of genetic and geographic variation has been discussed between Russian and Swedish authorities since the 1950s [14, 22]. The objective of the Russian-Scandinavian Larch Project is to study the genetics of the four main larch species within Russia,
Japanese forestry engineers successfully created hybrid larch F1 with high tolerance to various stress and also improved timber quality. Efforts are also made to establish larch plantations with considerations to biodiversity management, however, the outbreak of diseases of Japanese larch are reported in even UK [68]. Elite tree of larch was selected 270 clones from 20 to 40 years old plantations during 1955–1961; these clones were originated from central Japan. Among them we preferred to use Dahurian larch originated from the Kuril Islands but not from Sakhalin Island because leaf senescence is delayed in the Kuril one [18, 69].
Seed orchards were made by randomly planted with elite trees of Dahurian arch and Japanese larch, and provided seeds of hybrid larch F1 [14]. At 2000, we used hybrid larch F1 for plantation of 300 hm−2 year−1 (=800,000 planting stocks), however, these production activities were far from the demand of forestry industries [18]. This may be attributed to the low capacity of producing fertility of seeds of F1. The crossing ratio fluctuated mainly depending on the pollen father of Japanese larch; it reaches 56.3% in the good harvesting year while it was 23.2% in the bad harvest year, based on DNA marker [70]. On the way of selection of ideal F1, we isolated “Clean larch” (nick name of this new species) which showed a high growth rate and density in the stem (≒0.55); more than 20% larger than those of Japanese larch [17, 71].
In northern Japan, hybrid larch F1 (
Annual ring width and bulk density in several tree species planted in Hokkaido Island, Japan (Adopted from: Miyajima [
If we would plant larch with low density (standard planting density is 3000 ha−1), we can keep commercial important wood strength. This means we can save our labor power in weeding in the initial stage of planting. Regional Forestry Institute proposes low-density plantation from 1,500 to 1,000 hm−2 [18]. With low density, we can expect the invasion of several kinds of species that regenerate at open gaps. As efforts are also being made to establish plantations with considerations made to biodiversity management, the invasions of these gap species may be beneficial. In addition, topics on diseases of Japanese larch in the UK should be considered [68].
Clear-cut harvesting is one of the mainly performed forest management methods but is it considered to be the cause of large CO2 emissions. Understanding how this form of harvesting or logging affects site-specific CO2 balance is important for determining a considerate management method, however, data on how timber harvesting affects the CO2 balance of the ecosystem is still limited (Figure 11).
Concept of the forest CO2 balance after the harvesting from a spare mixed stand to make new plantation of hybrid larch F1 (a view in mid-October in yellow color) at Teshio Experiment Forest located at northern most Japan (Takagi et al. [
An experimental clear-cutting and plantation establishment study have been conducted in a cool-temperate mixed forest in northern Japan [73]. Before planting a the promising F1 (
We focus on the effects of environments (light, water) on larch species in Far East Russia to understand further responses of larch to the rapid change of environment including pollutants.
One of the topics will be described in this section to understand functional traits of larch in permafrost habitats (limited precipitation but rich in water via permafrost) in a continental climate, for example, Siberia (Russia): needle CO2 assimilation, respiration, and intra-tree carbon transfer using 13C labeling of mature larch trees. In China, the ecophysiological study is very limited but most studies were oriented CO2 flux monitoring to contribute CO2 balance in the atmosphere [74] but the acute estimation of non-photosynthetic organs [75] and soil respiration under different land-use [56]. Here we mainly focus on the ecophysiology of central Siberia studies.
The study area locates in the larch ecosystem (
Tura site layout (A), needle CO2-exchange measurement (B), whole-tree 13C-labeling experiment in June 2014 (C) and 13C-labeled mature larch tree inside the chamber (D) [
At Tura site, nine mature larch trees were 13C-labeled using whole-tree chambers (Figure 12C and D) in 2013–2014 (three trees in August 2013 and six trees in June and July 2014) [77]. A transparent plastic chamber (film thickness = 125 μm) was specifically designed to label the whole crown of the mature larch trees (about 104-year-old as of 2013). The chamber size (about 7 m3) was related to the dimensions of the target trees. Mixing fans were used to enable uniform distribution of 13C-labeled CO2 inside the chamber and for regulation of the inner air temperature and humidity, to prevent the photosynthetic apparatus from damaging due to the high temperature, which is expected in the closed chamber under intensive insolation [78, 79]. The 13C-labeling procedure is described by Masyagina et al. [77].
During the growing seasons (05 August 2013–19 September 2013 and 14 May 2014–15 September 2014), we sampled larch organs and tissues (brachiblasts: short-shoot needles; auxyblasts: long-shoot needle), twigs, phloem, xylem, and roots) for isotopic analysis of bulk δ13C from 13C-labeled trees on the selected dates (−1 = before labeling), 0 (−1 = before labeling, 0 = day of the labeling, 1, 4, 8, 15, 28, 40, 60, 75, and 90 days after labeling). In the following years after labeling, the sampling was undertaken monthly from June to September (2013–2018). Needles have been collected from the sun-exposed position of the larch crown between 11:00 and 18:00 hours (sampling was not conducted on rainy days). After collection, the needles were inactivated with a microwave oven at the middle regime (ca. 350 Watt) for 3 minutes to stop enzymatic and metabolic activities [80] (in details, please refer to * part in Figure 12).
Seasonal CO2 exchange of larch needles of six non-13C-labeled larch trees in the mid-June, mid-July, and mid-August of 2013–2014 was measured using an infrared gas analyzer Walz GFS-3000 equipped with the chamber for conifers (3010-V80) with the inner area of 8 cm2 as described by Masyagina et al. [77] (Figure 12B).
Diurnal dynamics of needle CO2 exchange of larch trees were studied over the growing season of 2013–2014. CO2 exchange values varied seasonally from −3.6 to 8.9 μmol CO2 m−2 s−1 in 2013 and −3.9 to 9.1 μmol CO2 m−2 s−1 in 2014. Similar maximal values of photosynthetic rates for
Midday depression of photosynthesis has been registered almost in all studied trees except for one individual in July of 2013. The most profound depression was found in June of both years when soil water accessibility remains little due to the shallow active soil layer (<20 cm) and in July 2014. In the permafrost zone, the physiological activity of
Diurnal dynamics of photosynthesis slightly varied among months of the growing season, for example, its length per 24 hours varied in the range of 11–16 hours due to environmental conditions. For example, in June, photosynthesis was registered from 6 a.m. to 9 p.m. in 2013 or 7 p.m. in 2014; in July, photosynthesis was active from 5 a.m. to 8–9 p.m.; in August, photosynthesis lasted from 6 a.m. to 5 p.m. in 2013 and from 8 a.m. to 7 p.m. in 2014. Interesting, the average values of photosynthesis were on a similar level of ca. 1–3 μmol CO2 m−2 s−1 (Figure 13) in various months. In mid-July, we observed a slightly higher rate of CO2 assimilation compared to the rest of the growing season.
Differences in diurnal curves of needle CO2-exchange rate for different months of the growing season (June–August of 2013 and 2014) in permafrost habitats. Trends are loess regressions. Grey shadows represent confidence intervals (standard error) of the regression.
To understand how C is traveling and allocating within a larch tree, we conducted several 13C labeling experiments at the beginning (June), in the middle (July), and at the end (August) of growing seasons of 2013 and 2014. Here, we will discuss only June-labeled trees, namely labeled on June 10–12, 2014. The main C-accepting tree organs were needles and long shoots; their enriched δ13C values achieved about 1700‰ in several hours after the 13C-labeling experiment completion (Figure 14). Our study showed similar CO2 assimilation capacity that resulted in the insignificant variation in 13C excess (about 136 ± 1% [mean value ± SE], CV = 4%, unpublished) in needles among the trees labeled in various periods of the growing season (mid-June, mid-July, and mid-August) in the day of the 13C-labeling experiment. It is a very interesting phenomenon since we found high variation in the environmental variables [77]. The 13C-enrichment of phloem, xylem, twigs, and roots did not exceed 500‰ just after the labeling experiment (Figure 14).
Dynamics of normalized δ13C (mean ± SE) over 2014–2018 in various organs and tissues (short-shoot needles: brachiblasts, long-shoot needles: auxyblasts), twigs, phloem, xylem, and roots) of larch (
In the year of the 13C-labeling experiment, the highest decay rate of δ13C was observed in needles and long shoots (Figure 14, panel 0). Two months after the 13C-labeling experiment there were peaked δ13C values (about 150‰) found in phloem due to intensive transfer of C at that time. At the end of the growing period of 2014 (year of a 13C-labeling experiment), the average δ13C values in yellow needles and long shoots were ca. 300‰, in twigs and wood (phloem and xylem), were ca. 21‰, and in roots were about −14‰. Such a high build-in C amount in senesced larch needles plays an important role in the metabolism of soil microbiota, including mycorrhiza, since it is an easy-destructive substrate.
Enriched δ13C values have been observed in studied tissues of trees at least over 4 years after 13C-labeling experiments (Figure 14, panel 1–4). At the beginning of the following growing season on 23 May, 2015, we registered enriched δ13C values (from −22 to 49‰) in all larch organs and tissues. The most 13C-enriched organs were needles, long-shoot needles, phloem, and twigs. It pointed to the intensive usage of the last-year C reserves in the early spring (bud-break period) for growth processes that confirms our previous results [77]. In other words, carbon is being involved in the exchange processes within a tree for a long time. However, Kagawa et al. [85] showed that after 2–3 years, there was little 13C excess left in the needles of larch saplings. These differences from our results may be due to the age differences since Kagawa et al. [85] 13C-labeled saplings of larch of heights of 10–73 cm.
At present, Dahurian larch (
Forest dynamics of larch in NE China is strongly regulated by forest fires [46, 57]. Stand density in the young and middle-stage (around 100 years) is relatively high (about 2,300 hm−2), but it sharply decreased over 100 years after the fire, and reached about 1,500 hm−2. The aboveground was estimated to be around 115 Mg ha−1. There was an altitudinal gradient of above biomass at Daxingan Mt. range (latitude 47 N to 52 N from 85 to 42 Mg hm−2, respectively), and 32 Mg hm−2 at Tura in Siberia (N62) [46]. Ecosystem productivity of China to Siberia decreases sharply with increasing latitude (Figure 15b) accompanied by an increase in shoot/root ratio [55].
Biomass of stem and net primary production (NPP) (a), latitudinal gradation and strand productivity or ecosystem productivity (b) (Modified from: Wang et al. [
Under the government of China’s environmental program known as Returning Farmland To Forests (RFTF = NFCP), about 28 million hectares of farmland have been converted to tree plantations. This has led to a large accumulation of biomass carbon, but less is known about underground carbon-related processes [56]. One permanent plot (25 years of observation) and four chronosequence plot series comprising 159 plots of larch (
This SOC accumulation rate (96.4 gm−2 year−1) can take 39% of the total carbon sink capacity [net ecosystem exchange (NEE)] of larch forests in this region and the total soil carbon sequestration could be 87 Tg carbon within 20 years of plantation by approximating all larch plantations in northeastern China (4.5 M hm−2), showing the importance of soil carbon accumulation in the ecosystem carbon balance. By comparison with the rates of these processes in agricultural use, the RFTF program of reversing land use for agriculture will rehabilitate SOC, soil fertility, and bulk density slowly (69% of the depletion rate in agricultural use), so that a much longer duration is needed to rehabilitate the underground function of soil via the RFTF program. Global forest plantations on abandoned farmland or function to protecting farmland are of steady growth and our findings may be important for understanding their underground carbon processes.
However, climate change has significantly affected the geographical distribution, population pattern and community productivity of
In northern Japan, Japanese larch (
Izuta [86] well summarized the current condition of the impact of environmental pollution on forest and farmland ecosystem. Since the 1960s, with the rapid economic development, air pollutants have impacted forest health and vigor in NE Asia [87]. SOx pollutants were reduced by desulfurization equipment during the 1970s; however, NOx including precures of O3 has hardly decreased because it is mainly produced by traffics [86]. Lockdowns applied amid the Covid-19 pandemic may decrease the rate to about 7 ppm year−1 between 2019 and 2020 as found in O3 emission in Europe [88]. Finally, we also discuss ECM under environmental change.
Effects of environmental changes on larch growth under elevated atmospheric CO2 concentration [CO2]. Globally, [CO2] has been increasing steadily since the Industrial Revolution. As CO2 is a resource for photosynthesis in green plants, an increase in [CO2] appears to be favorable for photosynthesis and the growth of trees. Although net assimilation rate and growth of trees were enhanced by elevated [CO2], the positive effects on light-saturated photosynthetic rate (Psat) do not persist over the long term [87]. Trees usually acclimatize to elevated [CO2] conditions. The Psat of plant species grown at elevated [CO2] decreases with time to the same level as that at ambient [CO2], which was found by Tissue and Oechel [89]. This trend was especially observed under severe conditions, for example, infertile soil, root restriction, and/or dilution of nutrients in the plant body [87]. This phenomenon is called “down-regulation” or photosynthetic adjustment [87, 89].
We should also consider the combined effects of high [CO2] and N deposition as a promoter of tree growth [90]. Physiological effects of nitrogen deposition on CO2 fixation are summarized as follows: Eguchi et al. [91] studied the photosynthesis of 2-year-old Japanese larch seedlings raised under ambient [CO2] (360 μmol mol−1) and high [CO2] (720 μmol mol−1), using environmental control growth cabinets (Phytotron). They found that high [CO2] increased the light and CO2-saturated photosynthetic rate (Pmax) of seedlings and changed the inner structure of needles of the seedlings grown in high-nutrient soil. The internal mesophyll surface area per unit needle surface area (Ames/A or Smes) increased with high [CO2], leading to a reduction in diffusion resistance of CO2 [91]. They concluded that the increase in the photosynthetic rate at high [CO2] was mainly due to easier transport of the CO2 to chloroplasts in needles.
Growth response and nutrient status of 2-year-old Japanese larch seedlings raised under different [CO2] during two growing seasons were determined by using an open-top chamber (OTC) [92]. At the end of the second growing season, high [CO2] increased the total biomass of Japanese larch seedlings, while only root biomass increased by elevated [CO2] was detected at the end of the first growing season. The different [CO2] levels did not give rise to any difference in nutrient concentration in the plant body, or in mycorrhizal formation in roots of seedlings. The greater total biomass under high [CO2] was due mainly to the increased root biomass during the first growing season, allowing better absorption of nutrients and stimulation of growth during the second growing season [92].
The xylem structure of Japanese larch seedlings under a combination of two [CO2] and nutrient regimes in phytotron for one growing season [91, 93]. Stimulation of secondary growth by high [CO2] was observed only with the high nutrient treatment. High [CO2] also increased the stem base diameter and changed some anatomical features of the tracheids, especially cell diameter. Development of more branches was observed for
Ozone (O3) in the troposphere is recognized as a widespread phytotoxic air pollutant. Since even ambient levels of O3 adversely affect growth and physiological functions, such as photosynthesis, of forest tree species, this gas is considered to be one of the most important factors involved in forest decline and reducing photosynthetic production in the USA, Europe, and Japan [10, 94]. The effects of oxidants on plants have been studied since the 1940s and have been reported that ozone generates reactive oxygen species such as O2- and H2O2 in leaves, having adverse effects on fatty acids in protoplasm and proteins in leaf. Based on experimental studies, Japanese larch is relatively sensitive to O3 exposure compared with other tree species in Japan [95]. In general, sensitivity to O3 of plants is greatly affected by growth conditions, such as temperature, light intensity, and soil moisture and nutrient status.
Watanabe et al. [96] reported that the sensitivity to O3 of Japanese larch seedlings grown in soil supplied with N at 50 kg N hm−2 year−1 was less than at 0 and 20 kg N hm−2 year−1. Nitrogen-induced changes in sensitivity to O3 must therefore be considered in risk assessment of O3 toward Japanese larch. Since [O3] in Hokkaido is currently low, the negative effect of O3 on larch species in this area may not be serious at present. However, relatively high [O3], sufficient to induce a reduction in the growth of larch species, is estimated in other parts of Japan [95]. Furthermore, [O3] has been increasing in Japan over the last two decades [10]. This trend will continue with an increase in precursors of O3, such as nitrogen oxides and volatile organic compounds, especially in the East Asian region [10].
It is predicted that photosynthetic production in terrestrial plants of the northern hemisphere will be reduced by more than 20–30% due to O3 in the near future [94]. The effect of high [O3] on larch species should therefore be considered because larch is dominant species in northern hemisphere.
According to the recent NO2 trend in Asia [97], we should pay attention to the rapid increase in NO2 emission and also the Biological volatile organic compound (BVOC) of larch as a precursor of O3 [98].
Based on the statistics of EU (LRTAP: Long-range Transboundary Air Pollution) and US (EPA: Environmental Protection Agency), the NO2 emission from Asia reached about 43 Tg NO2 year−1 which is four times larger than that from EU or UAS (Figure 16). Therefore, we should know this evidence and try to give O3 tolerance to larch plantation as suggested by Watanabe et al. [96].
Yearly trend of NO2 emission of three regions. Data are cited from Akimoto [
The biomass of Japanese larch decreased at 80 ppb, but it was lower at low O3 (<5 ppb) compared to 25 ppb [100]. This phenomenon is regarded as hormesis [101]. As almost all practical production of larch seedlings is done in the suburbs, we tried to use ethylenediurea (EDU) to moderate the adverse effects of elevated O3 on larch seedlings [102]. An effective concentration of EDU is 400 mg EDU L−1 applied as soil drench it protects both Japanese and F1 plants against toxicities induced by exposure to elevated O3 for up to 3–4 years. Methods using container grown seedlings in forestry practices are including mushroom production.
Nitrogen is often a limiting resource for plant growth in the forest ecosystem [82], and N fertilization frequently results in increased photosynthesis and enhanced growth of trees. Excessive amounts of N can nevertheless have a negative effect on the physiology and growth of the forest ecosystem. Forest declining due to high N load is suggested to have occurred in some coniferous forests, as recognized by the N saturation story [103]. N deposition has been increasing dramatically, especially in East Asia [11]. The main sources of atmospheric N deposition are anthropogenic emissions due mainly to fossil-fuel burning, and food production, relating mainly to agricultural waste and overuse of N-fertilizer. In Hokkaido, the annual deposition of N (NH4 + NO3) has increased to about 1.2 kg N hm−2 year−1 (as of 2012 [104]). Unfortunately, this increment will continue in the near future.
However, negative effects of N loading have not been observed yet. For example, N loading N load did not significantly affect the growth and net photosynthetic rate of Japanese larch seedlings grown in the soil of Andisol [96]. Furthermore, no growth and photosynthetic stimulation of Japanese larch and hybrid larch F1, grown in a mixture of clay loam, peat moss, and vermiculite with balanced fertilizer containing N and other nutrients such as P and K [4]. In contrast, growth and photosynthesis of Japanese larch seedlings grown in a mixture of clay loam and well-weathered pumice (nick name Kanuma), were stimulated by balanced fertilizer [92, 93]. Although the experimental periods differed among these studies, the soil type used in the experiment may be one of the important factors that induce the difference in the response of larch to N load (or fertilization).
Enzymes in N metabolism are affected by irradiance conditions [105], so that growth and photosynthetic responses of larch to N load are also regulated by light levels. Qu [4] examined the effects of different light intensities (8, 16, 32, and 100% of open condition) and two fertilization regimes (high/low) on seedlings of Japanese larch and F1 raised in a mixture of clay loam, peat moss, and vermiculite (the fertilizer was composed of balanced nutrients, like Hyponex: N:P:K = 6:10:5 and micro-elements). When light intensity exceeded 16%, dry-matter growth of Japanese larch was greater than that of F1, independent of fertilization regimes. However, the growth of Japanese larch in high-nutrient conditions was dramatically suppressed at 8% light intensity. This result indicates that high N load will make Japanese larch susceptible to shading, which was also found in nursery condition [106]. Ryu et al. [15] examined the effects of high N load on growth and ectomycorrhiza infection of Japanese larch, Dahurian larch, and their hybrid F1 seedlings growing in serpentine soil at low light intensity (8% against open) assuming forest floor conditions. It is well known that ECM symbiosis is important for the growth of host plants by assisting in the uptake of water and essential nutrients and by excluding heavy metals [34, 107]. No significant effects of N load on growth and infection by ECM were found. Inadequate light intensity and shortage of essential materials are suggested as possible factors for this phenomenon.
Several researchers indicated a fertilization effect of N load on other tree species such as Sugi-cedar (
In northeast Asia, pine and larch forests have declined in the vicinity of industrial or urban regions. Important factors causing this decline are the decrease in available nutrition and the increased metallic toxicity induced by soil acidification [86, 109]. Likely factors limiting the growth of plants in acid soil are the high acidity itself, phytotoxic metals such as aluminum (Al) or manganese (Mn), and reduced availability of important elements for plant growth [86]. However, infection with ECM fungi improves tolerance to environmental stresses by reducing the toxicity of metals [110]. The ECM role in growth responses of larch species under acid soil is therefore important in clarifying the effect of soil acidification on larches. The growth response of Japanese larch seedlings infected with several ectomycorrhizal fungi and raised under different soil acidification levels (proton concentrations of 10, 30, 60, and 90 mmol H+ kg−1) [109]. They quantified the ECM symbiosis that leads to improvement of the rhizosphere of larch seedlings. The results suggested that water-soluble phytotoxic elements (such as Al3+ and Mn2+) and essential elements (such as Ca2+, Mg2+, and K+) in soil increased with increasing soil acidification.
Concentrations of Al in the root and Mn in needles also increased. It is well known that Al3+ reduces the growth of roots, and Mn2+ replaces Mg2+ bound to the carboxylation enzyme (Rubisco; ribulose-1,5-bisphosphate carboxylase/oxygenase) and reduces photosynthetic activity [27]. Photosynthesis and the total dry mass of larch seedlings infected with ECM fungi were higher than in controls in all soil treatments. Also, the total dry mass of ECM seedlings was less at an acid level of 90 mmol H+ kg−1 than in unacidified ECM control seedlings; the ratio was about the same as without ECM infection.
As shown in Choi [109], severe soil acidification reduces the growth and photosynthesis of Japanese larch. At a lower level of acidification, ectomycorrhiza will help the larch to maintain growth, but will not help at severe acidification level. Based on the growth response to the concentration ratio of base cation (Ca2+, Mg2+, K+) to Al3+ (i.e., BC/Al ratio; BC/(Al + Mn) ratio) in the soil solution or water extract of soil, the sensitivity of Japanese larch to soil acidification is similar to that of Sugi-cedar, Red-pine and Sieblod’s beech [86, 109]. Soil acidification is important in the long term as, if the deposition rate of acid exceeds the rate of recovery of buffering capacity by weathering, the acid neutralization capacity of soil will be reduced in the future and soil pH will decrease. Considering that the lifespan of the tree is long, a serious reduction of growth of larch species due to soil acidification could occur in the future.
Since the 1950s, with the rapid economic development, air pollutants (NOx, SOx, Ozone: O3) and increasing CO2 have impacted forest health and vigor. The photosynthetic rate is usually reduced by elevated CO2 under root restricting conditions. SOx pollutants were reduced by desulfurization equipment during the 1970s; however, NOx has hardly changed because it is mainly produced by diesel cars [86]. NO2 is converted by O3 and NO via UV radiation [111]. In addition, atmospheric CO2 concentration [CO2] has increased since the Industrial Revolution and has reached around 418 ppm at the current rate of 2.2 ppm year−1. However, lockdowns applied amid the Covid-19 pandemic decreased the rate to about 7 ppm year−1 between 2019 and 2020.
Except for O3 (troposphere or ground-level O3), sufficient CO2 and adequate N are regarded as the productive atmospheric environment for forest trees. We summarize the effects of changing environment (CO2, N deposition, and O3) on the growth of larch and larch-ECM interactions.
In many cases, we found down-regulation of photosynthesis under elevated CO2, even in a FACE (Free Air CO2 Environment [87]) system. We expected ECM to act as a carbon sink and moderate down-regulation in photosynthesis, although for red pine seedlings inoculated with a kind of ECM (
The same trend was expected in larch. Hybrid larch F1 was planted in the FACE for 3 years and tended to fall down because of increased above-ground biomass [110]. After 5 years of CO2 fumigation in FACE, Japanese larch decreased biomass allocation to branches and increased it by about 20% in the stem compared with ambient CO2. In contrast, birch (
Ozone levels have been increasing around the northern hemisphere in the past several decades [94]. With the GIS method, Watanabe et al. [113] predicted that the growth of Japanese larch (
The specific difference in O3 sensitivity was examined between Japanese and hybrid larch F1 seedlings planted on the ground of OTCs (<5, 25, 45, and 80 ppb). The growth of both larches was significantly suppressed by 80 ppb (Figure 17; [14, 114]). The biomass of F1 seedlings decreased under 25 ppb, compared to <5 ppb, but this was due to its heterosis and maintained a similar biomass with Japanese larch seedlings in elevated O3 treatments.
Ozone concentrations and height in Japanese larch and its hybrid larch F1 (Adopted from: Kita et al. [
Plants usually close their stomata under elevated CO2 to reduce the absorption of O3. We examined the effects of elevated O3 (80 ppb) on the growth and ECM infection and diversity of hybrid larch F1 seedings under elevated CO2 in OTCs [37]. Under elevated O3, ECM infection rate and species diversity were reduced; however, these trends were moderated by elevated CO2 (600 ppm). Only early successional types of ECMs were found at ambient and elevated CO2. However, larch specialist
Infection rate and diversity of ECM of hybrid larch treated with combination of elevated CO2 (600 ppm) and O3 (80ppb) (Adopted from: Wang et al. [
This evidence suggests that a kind of ECM,
The combined effects of N and elevated O3 were studied in seedlings of two broadly distributed species: Siebold’s beech and larch, with the use of OTCs. The beech is classified as highly sensitive to O3 [95]. With increasing N (NH4NO3), O3 sensitivity of the beech increased in terms of Accumulated Exposure Over Threshold (AOT) of 40 ppb O3 (AOT40). In contrast, O3 sensitivity of Japanese larch decreased with increasing N up to 50 kg N hm−2 year−1. However, hybrid larch F1 had slightly increased O3 sensitivity with 50 kg N hm−2 year−1 under free-air O3 exposure [116], which may be due to decreased leaf life-span with N application [100].
In general, phosphorous (P) is the second most important nutrient after N; for the growth of hybrid larch F1, an adequate supply of P and N is required. Mg was the limiting element in the nursery of Hokkaido University [117]. In this edaphic condition, we examined the effects of N deposition (NH4NO3) on the growth of hybrid larch F1 for 8 years. Surprisingly, as a result, except for N application to F1 by the second year, almost no difference in the growth of F1 was found between the N treatment and the control (=no N application). Based on DNA analysis of the ITS region in symbiotic ECM, most of them infecting Japanese, Dahurian, and hybrid larch F1 were nitrogenous species [38], and were not altered by N application.
We expect a new CO2 sink when planting a new plantation in northern Japan. In Far East Russia and central Siberia [4, 5], they recognize the real essential role of the larch ecosystem on permafrost area, and they try to increase their timber quality to use genetically ideal larch and conserve permafrost ecosystem. Japanese larch is intensively used after considerable improvements in timber utilization. After harvest, we should make plantations with container-grown seedlings to save labor and attain high plantation efficiency. If we make new plantations with hybrid larch F1, we should ensure larch plantations do not increase N deposition under elevated O3. To make planting stock of F1, we should inoculate larch seedlings with ECMs (
In conclusion of this chapter, it can be said that urgent considerations should be made to moderate elevated ground-level O3 including dynamics of NO2 as precures of O3 against green infrastructure around big cities [5, 102], as larch forests is a vital component of global as well as local resources.
In this chapter, emphasis was made on the essential role of the larch ecosystem for environment conservation via highly forest management techniques. For this objective, we should point out detailed aspects of the larch forest ecosystem, specially developed on permafrost in Far East Russia and NE China. Recently, TV programs suggest the fear of melting of permafrost under changing environment in Alaska even though biological importance has been revealed back in the 1990s [23]. With the melting permafrost layer, many kinds of greenhouse gasses (CO2, CH4, N2O, NO2 as precures of O3, etc.) may be released and destroy our environment. Further knowledge on the ecophysiology of larch is still needed [50, 118, 119, 120], phylogeny [121], as the wise use of larch ecosystems will contribute to nature conservation and the sustainable use of the world’s natural resources.
We deeply appreciate the staff of Hokkaido Forestry Research Institute for their continuous support of our researches. Financial support in part by JST (No. JPMJSC18HB: representative researcher, M. Watanabe of TUAT and T. Watanabe of HU) and by the National Key Research and Development Program of China (2017YFE0127700; LY. Qu) are acknowledged. Moreover, O. Masyagina parts were supported by the Russian Foundation of Basic Research (grants no. 13-04-00659, 18-54-52005, and 19-29-05122), by the Russian Science Foundation (grant no. 14-24-00113), and the Academy of Finland (mobility grant decision no. 322679).
O.M. thanks the colleagues from the Sukachev Institute of Forest Alexander Klimchenko, Alexey Panov, Sergey Titov, Alexander Tsukanov, Anastasiya Urban, and Mashukov Dmitry for the various technical assistance during conducting whole tree 13C-labeling experiments in Tura Station (Evenkia, Russian Federation) in 2013 and 2014, and help with samples collection (2015-2018). O.M. appreciates the help during 13C analyses and valuable discussions of Katja Rinne-Garmston, Bartosz Adamczyk, Elina Sahlstedt, and Yu Tang from the Natural Resources Institute Finland (Luke), Alexey Artyukhov, Tatiana Udalova and Sergey Senchenkov from NRC Kurchatov Institute, Alexey Rublev (SRC Planeta), Oleg Menyailo, Alexander Shashkin, Alexander Kirdyanov, and Maria Meteleva from Sukachev Institute of Forest SB RAS, Federal Research Center “Krasnoyarsk Science Center SB RAS.”
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Baguley and Euphemia Leung",authors:[{id:"45751",title:"Prof.",name:"Bruce",middleName:null,surname:"Baguley",slug:"bruce-baguley",fullName:"Bruce Baguley"},{id:"45766",title:"Dr.",name:"Ephemia",middleName:null,surname:"Leung",slug:"ephemia-leung",fullName:"Ephemia Leung"}]}],mostDownloadedChaptersLast30Days:[{id:"53856",title:"Early-Stage Progression of Breast Cancer",slug:"early-stage-progression-of-breast-cancer",totalDownloads:1659,totalCrossrefCites:4,totalDimensionsCites:4,abstract:"Breast cancer can be defined as a group of diseases with heterogeneous origins, molecular profiles and behaviors characterized by uncontrolled proliferation of cells within the mammary tissue. Around one in eight women in the US will develop breast cancer in their lifetime, making it the second most frequently diagnosed cancer behind skin cancer [1]. In 2015, an estimated 231,840 cases of invasive carcinoma were diagnosed, and over 40,000 deaths were caused by breast cancer which accounts for almost 7% of all cancer mortality each year. In 2015, 60,290 cases of in situ breast cancer were diagnosed, representing over 14% of all new cancer cases among women and men. The steep increase in diagnosis of early‐stage breast cancer over the past 10 years is believed to be a result of more frequent mammography. However, since over half of these in situ lesions will not progress to invasive breast cancer, controversies have arisen about approaches to treatment and prevention of progression of early‐stage in situ breast cancer. Understanding the mechanisms of transition of normal breast to in situ pre‐neoplastic lesions and invasive breast cancer is currently a major focus of breast cancer research with implications for preventive and clinical management of breast cancer. In this review, we give an overview of current knowledge on the molecular and pathological changes that occur during early‐stage progression of breast cancer and describe some of the current models that are used to study this process.",book:{id:"5431",slug:"breast-cancer-from-biology-to-medicine",title:"Breast Cancer",fullTitle:"Breast Cancer - From Biology to Medicine"},signatures:"William Kietzman, Anna T. Riegel and Virginie Ory",authors:[{id:"190578",title:"Prof.",name:"Anna",middleName:null,surname:"Riegel",slug:"anna-riegel",fullName:"Anna Riegel"},{id:"190580",title:"Dr.",name:"Virginie",middleName:null,surname:"Ory",slug:"virginie-ory",fullName:"Virginie Ory"},{id:"190583",title:"MSc.",name:"William",middleName:null,surname:"Kietzman",slug:"william-kietzman",fullName:"William Kietzman"}]},{id:"23391",title:"Scleroderma and Breast Cancer",slug:"scleroderma-and-breast-cancer",totalDownloads:6155,totalCrossrefCites:0,totalDimensionsCites:0,abstract:null,book:{id:"329",slug:"breast-cancer-carcinogenesis-cell-growth-and-signalling-pathways",title:"Breast Cancer",fullTitle:"Breast Cancer - Carcinogenesis, Cell Growth and Signalling Pathways"},signatures:"Adamantios Michalinos, Michalis Kontos and Ian S. Fentiman",authors:[{id:"119147",title:"Prof.",name:"Ian",middleName:null,surname:"Fentiman",slug:"ian-fentiman",fullName:"Ian Fentiman"}]},{id:"52969",title:"Histopathological Characteristics: Clinical Course of Breast Cancer Subtypes Depending on the ER(+) (−)/PR(+) (−) Receptor Status",slug:"histopathological-characteristics-clinical-course-of-breast-cancer-subtypes-depending-on-the-er-pr-r",totalDownloads:1867,totalCrossrefCites:0,totalDimensionsCites:1,abstract:"Breast cancer patients were divided into separate groups, which were the estrogen receptor (ER)+/progesterone receptor (PR)+ HER2−, the ER or PR+ HER2−, the ER+/PR+ HER2+, the ER or PR+ HER2+, the ER−/PR− HER2−, and the ER−/PR− HER2+ groups. Patients with the ER/PR(+)/HER2− subtype breast cancers show better clinical prognosis compared to the hormone-negative, triple-negative (TN), and HER2+ subtypes. TN, HER2+ tumors in postmenopausal women were of higher grade, showing lymph node and lymphovascular invasion with poor prognosis in all case series. However, the ER+/PR−/HER2+ subgroup had the lowest survival rates in 2- and 5-year follow-ups. Comparison between the ER+PR+HER2+ and ER+PR−HER2− subgroups showed that HER2− status is an indicator of improved prognosis in long-term follow-up. Single hormone receptor (HR)(+) status, particularly HER2(−) cases, was in between the favorable and poor survival subgroups. The ER−, PR−, and HER2+ properties were found to be risk factors for frequent recurrences. In this chapter, breast cancer subtypes are compared with each other. Results from different studies highlight the importance of ER/PR/HER2 receptor variations in the choice of treatment and prognosis of breast cancer.",book:{id:"5431",slug:"breast-cancer-from-biology-to-medicine",title:"Breast Cancer",fullTitle:"Breast Cancer - From Biology to Medicine"},signatures:"Nilufer Bulut",authors:[{id:"189255",title:"Associate Prof.",name:"Nilufer",middleName:null,surname:"Bulut",slug:"nilufer-bulut",fullName:"Nilufer Bulut"}]},{id:"42313",title:"HER2-Driven Carcinogenesis: New Mouse Models for Novel Immunotherapies",slug:"her2-driven-carcinogenesis-new-mouse-models-for-novel-immunotherapies",totalDownloads:4463,totalCrossrefCites:2,totalDimensionsCites:2,abstract:null,book:{id:"2883",slug:"oncogene-and-cancer-from-bench-to-clinic",title:"Oncogene and Cancer",fullTitle:"Oncogene and Cancer - From Bench to Clinic"},signatures:"Cristina Marchini, Lucia Pietrella, Cristina Kalogris, Chiara Garulli, Federico Gabrielli, Elena Quaglino, Manuela Iezzi, Serenella M. Pupa, Elda Tagliabue and Augusto Amici",authors:[{id:"63448",title:"Dr.",name:"Manuela",middleName:null,surname:"Iezzi",slug:"manuela-iezzi",fullName:"Manuela Iezzi"},{id:"139607",title:"Dr.",name:"Augusto",middleName:null,surname:"Amici",slug:"augusto-amici",fullName:"Augusto Amici"},{id:"143496",title:"Prof.",name:"Cristina",middleName:null,surname:"Marchini",slug:"cristina-marchini",fullName:"Cristina Marchini"},{id:"143498",title:"Dr.",name:"Lucia",middleName:null,surname:"Pietrella",slug:"lucia-pietrella",fullName:"Lucia Pietrella"},{id:"143499",title:"Dr.",name:"Cristina",middleName:null,surname:"Kalogris",slug:"cristina-kalogris",fullName:"Cristina Kalogris"},{id:"143501",title:"Dr.",name:"Chiara",middleName:null,surname:"Garulli",slug:"chiara-garulli",fullName:"Chiara Garulli"},{id:"143502",title:"Dr.",name:"Federico",middleName:null,surname:"Gabrielli",slug:"federico-gabrielli",fullName:"Federico Gabrielli"},{id:"143503",title:"Dr.",name:"Maura",middleName:null,surname:"Montani",slug:"maura-montani",fullName:"Maura Montani"},{id:"143504",title:"Dr.",name:"Elda",middleName:null,surname:"Tagliabue",slug:"elda-tagliabue",fullName:"Elda Tagliabue"},{id:"155534",title:"Dr.",name:"Elena",middleName:null,surname:"Quaglino",slug:"elena-quaglino",fullName:"Elena Quaglino"},{id:"155535",title:"Dr.",name:"Serenella M.",middleName:null,surname:"Pupa",slug:"serenella-m.-pupa",fullName:"Serenella M. Pupa"}]},{id:"42310",title:"MLL Gene Alterations in Acute Myeloid Leukaemia (11q23/MLL+ AML)",slug:"mll-gene-alterations-in-acute-myeloid-leukaemia-11q23-mll-aml-",totalDownloads:5175,totalCrossrefCites:0,totalDimensionsCites:0,abstract:null,book:{id:"2883",slug:"oncogene-and-cancer-from-bench-to-clinic",title:"Oncogene and Cancer",fullTitle:"Oncogene and Cancer - From Bench to Clinic"},signatures:"Denisa Ilencikova and Alexandra Kolenova",authors:[{id:"140472",title:"Dr.",name:"Denisa",middleName:null,surname:"Ilencikova",slug:"denisa-ilencikova",fullName:"Denisa Ilencikova"},{id:"155307",title:"Dr.",name:"Alexandra",middleName:null,surname:"Kolenova",slug:"alexandra-kolenova",fullName:"Alexandra Kolenova"}]}],onlineFirstChaptersFilter:{topicId:"1075",limit:6,offset:0},onlineFirstChaptersCollection:[],onlineFirstChaptersTotal:0},preDownload:{success:null,errors:{}},subscriptionForm:{success:null,errors:{}},aboutIntechopen:{},privacyPolicy:{},peerReviewing:{},howOpenAccessPublishingWithIntechopenWorks:{},sponsorshipBooks:{sponsorshipBooks:[],offset:8,limit:8,total:0},allSeries:{pteSeriesList:[{id:"14",title:"Artificial Intelligence",numberOfPublishedBooks:9,numberOfPublishedChapters:87,numberOfOpenTopics:6,numberOfUpcomingTopics:0,issn:"2633-1403",doi:"10.5772/intechopen.79920",isOpenForSubmission:!0},{id:"7",title:"Biomedical Engineering",numberOfPublishedBooks:12,numberOfPublishedChapters:98,numberOfOpenTopics:3,numberOfUpcomingTopics:0,issn:"2631-5343",doi:"10.5772/intechopen.71985",isOpenForSubmission:!0}],lsSeriesList:[{id:"11",title:"Biochemistry",numberOfPublishedBooks:27,numberOfPublishedChapters:287,numberOfOpenTopics:4,numberOfUpcomingTopics:0,issn:"2632-0983",doi:"10.5772/intechopen.72877",isOpenForSubmission:!0},{id:"25",title:"Environmental Sciences",numberOfPublishedBooks:1,numberOfPublishedChapters:9,numberOfOpenTopics:4,numberOfUpcomingTopics:0,issn:"2754-6713",doi:"10.5772/intechopen.100362",isOpenForSubmission:!0},{id:"10",title:"Physiology",numberOfPublishedBooks:11,numberOfPublishedChapters:139,numberOfOpenTopics:4,numberOfUpcomingTopics:0,issn:"2631-8261",doi:"10.5772/intechopen.72796",isOpenForSubmission:!0}],hsSeriesList:[{id:"3",title:"Dentistry",numberOfPublishedBooks:8,numberOfPublishedChapters:129,numberOfOpenTopics:0,numberOfUpcomingTopics:2,issn:"2631-6218",doi:"10.5772/intechopen.71199",isOpenForSubmission:!1},{id:"6",title:"Infectious Diseases",numberOfPublishedBooks:13,numberOfPublishedChapters:107,numberOfOpenTopics:3,numberOfUpcomingTopics:1,issn:"2631-6188",doi:"10.5772/intechopen.71852",isOpenForSubmission:!0},{id:"13",title:"Veterinary Medicine and Science",numberOfPublishedBooks:10,numberOfPublishedChapters:103,numberOfOpenTopics:3,numberOfUpcomingTopics:0,issn:"2632-0517",doi:"10.5772/intechopen.73681",isOpenForSubmission:!0}],sshSeriesList:[{id:"22",title:"Business, Management and Economics",numberOfPublishedBooks:1,numberOfPublishedChapters:12,numberOfOpenTopics:2,numberOfUpcomingTopics:1,issn:null,doi:"10.5772/intechopen.100359",isOpenForSubmission:!0},{id:"23",title:"Education and Human Development",numberOfPublishedBooks:0,numberOfPublishedChapters:0,numberOfOpenTopics:2,numberOfUpcomingTopics:0,issn:null,doi:"10.5772/intechopen.100360",isOpenForSubmission:!1},{id:"24",title:"Sustainable Development",numberOfPublishedBooks:0,numberOfPublishedChapters:10,numberOfOpenTopics:4,numberOfUpcomingTopics:1,issn:null,doi:"10.5772/intechopen.100361",isOpenForSubmission:!0}],testimonialsList:[{id:"13",text:"The collaboration with and support of the technical staff of IntechOpen is fantastic. The whole process of submitting an article and editing of the submitted article goes extremely smooth and fast, the number of reads and downloads of chapters is high, and the contributions are also frequently cited.",author:{id:"55578",name:"Antonio",surname:"Jurado-Navas",institutionString:null,profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bRisIQAS/Profile_Picture_1626166543950",slug:"antonio-jurado-navas",institution:{id:"720",name:"University of Malaga",country:{id:null,name:"Spain"}}}},{id:"6",text:"It is great to work with the IntechOpen to produce a worthwhile collection of research that also becomes a great educational resource and guide for future research endeavors.",author:{id:"259298",name:"Edward",surname:"Narayan",institutionString:null,profilePictureURL:"https://mts.intechopen.com/storage/users/259298/images/system/259298.jpeg",slug:"edward-narayan",institution:{id:"3",name:"University of Queensland",country:{id:null,name:"Australia"}}}}]},series:{item:{id:"11",title:"Biochemistry",doi:"10.5772/intechopen.72877",issn:"2632-0983",scope:"Biochemistry, the study of chemical transformations occurring within living organisms, impacts all areas of life sciences, from molecular crystallography and genetics to ecology, medicine, and population biology. 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