Instituto de Investigación Lightbourn A.C.
Bionanofemtofisiología Vegetal Disruptiva
Fulvalene, Rotaxane and Catenane Compounds:
Ultraviolet Radiation Effects on Plants and its
Bioremediation
Lightbourn-Rojas L A1, León-Chan R G1, Heredia J B1, 2
1
Instituto de Investigación Lightbourn A.C. Bionanofemtofisiología Vegetal Disruptiva
Centro de Investigación en Alimentación y Desarrollo A.C. (CIAD) Unidad Culiacán
2
Abstract
There are several studies on climate change, which focus on different factors: the
increase in atmospheric CO2, droughts, variable amount of rainfall, sudden
temperature changes and the increase of ultraviolet radiation (UV) due to the
deterioration of the ozone layer by atmospheric contaminants. The increase of UV
radiation causes adverse responses in plants development, particularly in DNA and
in photosynthetic system, especially in photosystem II, therefore the loss of
photosynthetic efficiency and a foods reduction. Plants have developed several
defense systems which are related to the synthesis of anthocyanins. These
compounds can protect plant tissues by absorbing excess of light, UV radiation or
by their antioxidant capacity, scavenging UV produced reactive oxygen species.
However, sometimes these mechanisms are insufficient due to photosynthetic
deficiency; therefore we have developed a new plant nutrition technology, based
on fulvalene, rotaxane and catenane compounds. With this approach, an increase
in the uptake, storage and availability of monochromatic ray at 563 nm can be
achieved. This can induce the photosynthetic optimization and the reduction of
metabolic delays in the photosynthetic system. This would help to maintain the
plant metabolism and therefore the stability of the food production regardless of the
adverse environmental conditions.
Introduction
The climate of a planet is determined by its total mass, its distance from the closest
star(s) (in the case of the Earth, the Sun) and the chemical composition of its
atmosphere (González et al., 2003). The latest is the most variable factor, both
naturally and by the activities of the organisms that inhabit it, especially humans. In
recent decades there have been a wide range of environmental changes that are
affecting life on Earth, so there are a variety of studies on climate change, which
focus on different factors such as the increase in atmospheric CO2 concentration,
melting icecap, drought, change in rainfall patterns, wind speed, sudden
temperature change, global warming and increased ultraviolet radiation, among
others (Bellard et al., 2012).
Plants are the organisms more exposed to environmental changes because
they can not migrate from where they develop, so they are essential baseline to
understanding the impact of climate change on Earth. Changes in the environment
to produce a negative impact on growth and development of plants are considered
as stress factors (Bray et al., 2000). This can be classified into primary stress,
when the stress factor directly affects the development of plants, and secondary
stress, when the stress factor provides generation of reactive oxygen species
(ROS) which adversely affect the metabolism of the plant (Ahmad y Prasad 2012).
The effects of climate change on living organisms can be classified into four
categories (Gonzales et al., 2003): 1) geographic distribution (tendency of some
species to move), 2) adaptation (micro-evolutionary changes in situ) 3)
physiological (photosynthesis, respiration, growth) and 4) phenological (changes in
the life cycles such photoperiod effects, cold hours, etc.). Therefore, changes in
radiation and temperature are factors that have more impact on the organisms
present on Earth, especially in plants, which are the basis of life energy on the
Earth, because they can transform solar energy into chemical energy , which is
taken by the rest of the organisms as food.
The plant growth is defined as an increase in dry matter, while development
is the increase in the number and size of their organs by division and/or cell
expansion: leaves, sticks, swords, flowers, roots, etc. The growth rate is
proportional to the product of the rate and efficiency of the catabolic activity to
convert photosynthates to structural biomass, therefore, plant growth is extremely
temperature sensitive (Lightbourn, 2011a; Źróbek-Sokolnik, 2012). On the other
hand, solar radiation (electromagnetic radiation) is one of the most important
factors in the growth and development of plants (Carrasco-Ríos, 2009), and is
involved in many important processes such as photosynthesis, phototropism,
photomorphogenesis, opening stomata, soil and temperature, etc. (Salisbury and
Ross, 1994; Castilla, 2007).
Solar radiation can be divided into three main ranges of wavelength:
infrared, visible and ultraviolet radiation (UV) (Castilla, 2007). UV radiation provides
a higher energy level that can adversely affect the metabolism of any organism.
This type of radiation is partially absorbed by the ozone layer. However, the
increasing of certain gases such as chlorofluorocarbons (CFC's) resulted in the
deterioration of the protective layer, therefore lead to an increase of UV radiation at
the Earth's surface (Hollósy, 2002).
The stress caused by increase of UV radiation triggers a range of
responses, such as alterations in gene expression and changes in cell metabolism,
which has influence on growth, development and production of plants. The length
and severity of stress, as well as the characteristics of the plants, their stage of
development, the affected tissue and genotype would influence on the answers
plants can present (Bray et al., 2000).
One of the most commonly response presented on stressed plants induced
by UV radiation is the synthesis of flavonoids, such as anthocyanins, which may be
due to its ability to absorb UV light or to the antioxidant capacity that these
compounds provide to reverse oxidative damage caused by UV radiation on cells
(Mazid et al., 2011).
However, these mechanisms could be insufficient due to photosynthetic
deficiency induced by UV radiation. Therefore, a new technology in plant nutrition
has been developed which optimizes the photosynthetic efficiency by maintaining
more available the power provided by the monochromatic ray of 563 nm.
Temperature
In recent decades there has been a rise in temperature that is seriously
affecting the biological processes on Earth. This temperature increase is
widespread over the globe, such as in the Arctic, where the average temperature
has increased at almost twice as fast as the global average of the last one hundred
years (IPCC, 2007).
The temperature is not a measure of amount or concentration of a
substance or total energy. The temperature measures the molecular movement,
which means, the kinetic energy of the molecules within the system. Consequently,
the velocity indices of all elemental reactions increase exponentially with the
temperature increments (Lightbourn, 2011a). The thermodynamics first law refers
that the heat added to a system minus the work done by this, it will produce a
change in the internal energy of the system:
ΔE = q - W
where ΔE is the change in internal energy of the system, q is the amount of
heat added and W is the work carried out by the system, in this case we refer to
plants as the system in question. If q < W then the internal energy of the plant
decreases down to death, while if q >>> W then the heat inside the plant will
increase causing denaturation of its components (Lightbourn et al., 2012).
Therefore, a change of a few Celsius degrees leads to a significant change in the
growth rate, and this is because there is not a range in which the temperature
stops changes that affect the growth rates, so it is incorrect to talk about stress
ranges by temperatures, being correct when talking about stress by temperaturetime (Lightbourn, 2011a).
The stress caused in plants by temperature is classified into three types: 1)
cold damage, 2) freezing damage and 3) by high temperatures. This is because
each species or variety has, at any given state of its life cycle, a minimum
temperature below which does not grow, the optimum temperature (or temperature
range) which grows to a maximum rate and temperature above the maximum
which will not grow and may even die (Salisbury y Ross, 1994; Źróbek-Sokolnik,
2012). Therefore, the temperature is defined as an environmental factor that
significantly affects biological processes in all organisms because it will primarily
modify the properties of the membranes, the levels of enzymatic activity, speed up
chemical reactions, as well as affecting the phloem, xylem and cytoplasm solutions
(Taiz y Zeiger 2002; Źróbek-Sokolnik, 2012).
The membranes are in one of three stages depending on the external
environment: 1) as a crystalline liquid phase, which represents the range of fluidity
in which the membrane and its components work naturally, 2) as a solid gel, which
represents a membrane that retains its shape but is rigid and therefore not
functional, 3) and hexagonal and cubic phases, which represents the disruption of
the membrane caused by extreme environments (Nilsen and Orcutt, 1996). In the
first stage we have mentioned a balanced equation of thermodynamics first law,
while cases two and three are derived from an imbalance between the work of the
plant and the added heat (Lightbourn et al 2012).
The increase in temperature causes a greater fluidity in the membranes,
causing problems in cell functions, mainly in mitochondria and chloroplasts
(Allakhverdiev et al., 2008). Therefore, the deleterious effects that high
temperatures cause on plants mainly occur in photosynthetic functions and
thylakoid membranes. The three more sensitive photosynthetic sites to heat stress
are the carbon assimilation process, the ATP generation and the photosystems,
mainly photosystem II complexes (PSII), which are the most labile part of the
photosynthetic system to the heat effects (Salisbury and Ross, 1994; Allakhverdiev
et al., 2008). Also, the synthesis of various thylakoid membrane proteins is
extremely reduced during elevated temperature exposure (Süss and Yordanov,
1986), i.e. the apoprotein reaction center of photosystem II (P680), the sub-units α
and β of the ATPase synthase, cytochrome ƒ, cytochrome b559 and the apoprotein
from the center of the CP47 antenna complex (Santarius, 1973). This causes a
great disruption of PSII leading the plant inability to produce energy (ATP) from
photosynthesis. In general, the photosynthetic activity is stable until 30 °C but
dramatically decreases above this temperature until a complete inhibition is
reached at 40 °C (Carpentier, 2005).
Moreover, the increase chloroplasts membrane fluidity allows the ATP
molecules to go through more easily from citosol to chloroplasts (Carpentier,
2005). ATP is used in chloroplast to carry out the synthesis of carbohydrates in
mature plants, but in plants in growth phase, the ATP is used predominantly for
proteins and nucleotides synthesis, for which is required greater amount of energy
(Salisbury and Ross, 1994), so that in the photosynthetic system inefficiency
caused by stress is necessary to obtain energy from other sources to continue the
plant development until reserves will allow it. Therefore, the morphological
symptoms presented in heat stressed plants may include sunburn on leaves,
branches and stems, senescence and abscission of leaves, stem growth inhibition
and roots, damage and fruit discoloration, less production, cell size reduction,
stomatal closure and reduction of transpiration to prevent dehydration (Waheed et
al.; 2007 Mitra and Bhatia, 2008).
The observed increase in global average temperatures since the midtwentieth century is mainly due to the observed increase in concentrations of
anthropogenic greenhouse gases, which was found at 70% from 1970 to 2004; this
increase is due to the higher emission of these gases in relation of its
decomposition. Human activities result in emissions of four long-lived greenhouse
gases: carbonic anhydride mostly known as carbon dioxide (CO2), methane (CH4),
nitrous oxide (N2O) and chlorofluorocarbons (CFC's, group of gases containing
fluorine, chlorine or bromine). Increased CO2 concentrations are due primarily to
fossil fuel use, the CH4 is predominantly due to agriculture and fossil fuel use and
N2O increased is mainly due to agricultural activities (IPCC, 2007). The increase in
some of these compounds causes the degradation of the ozone layer, allowing a
greater emission of ultraviolet rays at the Earth surface, which also inferred in
plants development (Björn and McEnzie, 2008).
Ultraviolet Radiation (UV)
The UV radiation corresponds to a wavelength range of 200 to 380 nm. This
radiation is low when the sun elevation above the horizon is low and to low altitude.
UV radiation represent about 9% of the solar total radiation energy and can be
divided into UV-A (320 to 280 nm) skin tanning radiation, UV-B (290 to 320 nm)
responsible of skin cancer, and UV-C (200-290 nm) which is potentially hazardous
but almost completely absorbed by the ozone layer (Castilla, 2007, Prado et al.,
2012). The absorption coefficient of ozone decreases rapidly at wavelengths above
280 nm and approaches zero around 330 nm (Hollósy, 2002). Although the
stratospheric ozone determines the amount of UV radiation that reach the Earth
surface, its level is significantly affected by variations in latitude and altitude. The
level of UV radiation over tropical latitude is higher than in temperate regions due
to lesser atmospheric UV absorption determined by the solar angle and the ozone
layer itself, which is thinner in equatorial regions (Jaakola and Hohtola, 2010;
Prado et al., 2012).
In 1987, it was established the Montreal Protocol on "Substances that
deplete the Ozone Layer" to carry out the reduction of these compounds in the
atmosphere, mainly CFCs; however, the deterioration continues increasing to 0.6
% yearly (Prado et al., 2012). In general, every 1 % of reduction in the ozone layer
results in an increase of 1.3 to 1.8 % of UV-B radiation (Hollósy, 2002). Most
studies concerning that the effects of UV radiation increases are focus on UV-B
radiation, however, the presence of UV-C radiation has been show, even within
plastic greenhouses (León-Chan, 2012), so there are some studies that provide
UV-C to study their effects on plants (Mahdavian et al., 2008; Sarghein et al., 2008;
Katerova et al., 2009).
UV radiation can inhibit photosynthesis by altering gene expression and by
damaging the parts of the photosynthetic machinery (Smith et al., 2009). Sites that
are affected by this type of light are the light collector complex II (LHCII), the PSII
reaction center and PSI acceptor. However, most studies have demonstrated that
PSII is more sensitive to UV radiation as compared to PSI; this is due to the
chemical changes which produces the UV radiation on amino acids with double
bonds of the PSII proteins (Carrasco-Ríos, 2009). The aromatic amino acids such
as phenilalanine, tryptophan and tyrosine, as well as cysteine, cystine, and
histidine, would provide to proteins the characteristic of absorbing UV and thereby
the property to be modified (Hollósy, 2002). The amino acid histidine is present in
the PSII D1 protein, which contains chlorophylls linked to it (Taiz and Zeiger,
1998), therefore, the conformational changes causing by UV on these proteins will
liberate chlorophylls, facilitating their photo-oxidation (Mahdavian et al ., 2008).
The UV radiation also induces the loss of enzymes activity involved in the
Calvin cycle, especially on the 1,5 diphosphate carboxylase (Rubisco) which
catalyzes the CO2 incorporation. Another effect of UV radiation is the production of
reactive oxygen species (ROS), which also act on the denaturation of proteins;
moreover, ROS are involved in the lipoperoxidation processes from the plasma
membrane (Björn and McEnzie, 2008, Carrasco-Ríos, 2009). However, ROS can
also initiate signals stress responses to UV, including enzyme activation, gene
expression, programming cell death, etc. (Jaspers and Kangasjärvi, 2010).
The DNA is also sensitive to UV-B and UV-C, because these photons
promote π-π transitions in nitrogenous bases that constitute the nucleotides,
altering the normal establishment of chemical bonds. This mainly causes the
formation of cycle butane pyrimidine dimers (CPD) produced by the dimerization of
adjacent pyrimidines (TT, TC, CT or CC), and produce other compounds known as
(6-4) photo products (Björn and McEnzie, 2008; Carrasco Rivers, 2009). The
biological effects of these lesions are variable, since in some cases replication in
the lesion is stopped, while in other cases the replication continuous, thereby
promoting mutations. Therefore, these products are the leading causes of cancer
(Björn and McEnzie, 2008).
Plant Responses to Ultraviolet Radiation
The plants exhibit different responses to environmental stresses like UV
radiation exposure. Under these conditions, plants would show the presence of
wax cuticle deposition and trichomes that function as radiation reflectors; leaf area
reduction and increased of sheet thickness to reduce the damaged area; changes
on stomatal density, reduced of stems elongation, changes in branching pattern,
the synthesis of secondary metabolites with the ability to absorb UV light, as well
as alterations in plant-pathogen plant-predator interactions and gene expression
(Prado et al., 2012).
The synthesis of secondary metabolites of the phenylpropanoid pathway
has been widely studied as a defense mechanism to counteract the deleterious
effects of UV radiation produced in plants. Among these compounds there are
phenolic acids, insoluble polyphenols and flavonoids such as anthocyanins. Today
anthocyanins are the most studied flavonoids usually referred as the compounds
capable of reducing the photo-oxidative damage. These compounds stay mainly in
the epidermis cells, and are also being responsible for a variety of colorations in
plant tissues (Castañeda-Ovando et al., 2009).
Some authors mention that the tissues most exposed to the sun show
higher anthocyanin content, presenting a high variability of the content of these
compounds from leaves or fruits of the same plant (Salisbury and Ross 1994;
Lightbourn et al., 2008; Steyn, 2012). Here, the hypothesis about the anthocyanin
function in plants are showed: 1) protection of chloroplasts from excessive light,
especially in plants in development process or that have developed under shaded
conditions (Oren-Shamir, 2009); 2) protection against UV radiation, by the ability of
these compounds to absorb this type of radiation and, 3) the antioxidant capacity
that these compounds have, several times greater than some of its antioxidant
vitamins analogues. This antioxidant capacity could reduce the damage caused by
ROS generated by UV radiation (Hatier and Gould, 2009).
Some researches have shown an anthocyanins increase by effect of UV
radiation on different plant sources and in different development stages
(Mahadavian et al., 2008; Saghein et al., 2008, Guo and Wang 2010; Leon Chan,
2012). Therefore, there are investigations about the induction of some enzymes
involved in anthocyanin synthesis by radiation effect, finding an increase in the
activity of some of them, among which are the phenylalanyl ammonia lyase (PAL),
chalcone synthase (CHS), chalcone isomerase (CHI), dyhydroflavonol 4-reductase
(DFR), anthocyanin synthase (ANS), flavonone-3-hydroxylase (F3H), etc. (Tsukasa
et al. 2000; Hao et al., 2009; Guo and Wang 2010). With these facts, it has been
proven the involvement of these compounds on UV protection effects; besides
obtaining more information about the expressing routes and thereby creating new
alternatives that will promote the survival of plants against UV radiation stress (Guo
et al., 2008).
Other Environmental Impacts by Ultraviolet Radiation
The changes in plants metabolism due to the increase of UV radiation not
only reduce the life of plants affected, because the reduction of food production
would cause great problems in the life of other organisms, particularly in humans;
as well as other issues like the balance of certain cycles, such as the carbon cycle
that can be severely affected by the changes in damaged plants and their capture
mechanism, as well as photosynthesis, carbon storage and respiration, among
others (Zepp et al., 2007). The classification of the UV radiation impact on the
Earth's surface is related to direct effects such as photosynthesis inhibition and the
carbon cycle balance; and indirect effects such as the alteration of the chemical
composition of plant foods which will also affect the decomposition of organic plant
matter in the soil by other organisms (Smith et al., 2009).
The increase of anthocyanins in plant tissues can cause changes in plants
interactions with other organisms. These interactions include attracting pollinators
and frugivores as well as herbivores and parasites repellents (Lev-Yadum and
Gould, 2009). It has also been observed some reduction of pathogenic attack,
therefore the increase of these compounds in certain case could be beneficial
(Paul et al., 2012). However, the production of these compounds may result in a
high energy cost to the plants, and it can become even greater considering the
deficiencies in energy production of plants whose have been damaged by UV
radiation; so there is a difficulty to the plant in order to sustain this defense
systems, as well as to reduce the production of plants with this stress (Wargent
and Jordan, 2013). This reduction in food production may become even a greater
problem, considering the increase in world population that is estimated at 9 billion
of people by 2050 (The Royal Society, 2009).
The leaves commonly that contain anthocyanins absorb more light in the
visible green and yellow region spectrum regarding those leaves which do not
contain it; however, is unknown this energy function (Hatier and Gould, 2009). This
energy could be used in repair mechanisms or photosynthesis optimization,
whereby the plant can continue to perform its metabolic activities with the least
possible deficiency; nevertheless, this mechanism may occur deficient with
nutritional techniques that have to now, since the increase in certain nutrients
appears not to be improved in plants that are damaged by UV light, because it only
considers some basic elements and excluding that plants would use many more
elements to carry out their functions (Lightbourn et al., 2011; Singh et al., 2012).
On the other hand, there is an increase in the use of plastic greenhouses in
order to reduce the risk of pathogen attack, and also to reduce high UV radiation
levels, therefore preventing from reaching and damaging the plants. However,
when the light passes from one medium to another, it suffers inverted cycloid
deviations namely tautocrony producing dicroism and birefringence that affects the
polarity and intensity of the light beam incident and refracted which consequently
alters the photosynthetic phenomenon. This can be quantified as a function of light
energy, starting from the basic conceptions and traditional until the logic formality
given by the mathematical complex of variations calculation in cycloid curves of
mathematical analysis (Lightbourn, 2010).
Reducing Plant Damage
It has been demonstrated that with the application of a high dose of
photosynthetically active radiation (PAR) in conjunction with low levels of UV-B
radiation, Rubisco levels are unaffected; therefore, a sufficient amount of PAR
radiation diminishes the UV radiation adverse effects (Hollósy, 2002). Furthermore
inhibition of PSII activity in intact leaves during heat stress at 40 °C is mitigated if
performed during a low-intensity illumination. This is because light is responsible to
activate the adaptation mechanisms of the photosynthetic apparatus in the
presence of stress temperature, especially photosystems repair, which require a
low light intensity to carry out the protein phosphorylation and stimulation of diverse
enzymes activity. In contrast, a strong light accelerates the PSII deterioration
(Carpentier, 2005; Allakhverdiev et al., 2008).
Actually a new technology has developed in plant nutrition that consists on
clusters of selenium, nickel, titanium and polioxomolibdato. This is in fulvalenic
rotaxane-catenananica base, generating orthogonal sequence dendrimers that are
intra-tilacoidic nanosomes, which enables to optimize the photosynthetic efficiency
by capturing, storing and maintaining more available power provided by the
monochromatic beam of 563 nm. Therefore, induces the photosynthesis
optimization, serving as a light reserve at chloroplasts level. This helps to maintain
the plant metabolism, which results in phytotaxic stability, and therefore, stability of
production, irrespective of any adverse conditions such as UV radiation stress
(Lightbourn 2011b).
Furthermore this technology contains zinc as the principal element, which is
required for growth hormones synthesis (cytokinins and auxins), besides
participate in chlorophyll production and possibly prevent its destruction (Salisbury
and Ross, 1994), thereby further reduce the damage caused by high temperatures
and UV radiation.
This compound is applied by foliar absorption and involves an innovation in
signaling and synchronization cell, because provide continuity in photosynthetic
energy uptake and transfer, due to that clusters absorb and store energy.
Furthermore, owing of these clusters not interrupt the metabolism on account of
darkness, there are no delays in the formation and maintenance of plant tissue
which means the total dejection of metabolic delays and consequences translated
into structural failures, metabolic, energetic and homeostatic that directly affect the
quantity and quality of biomass (Lightbourn, 2011b).
Besides the damage due to overheating and/or UV radiation, may be
metabolic delays, which are because when the active photosynthetic cycle has
been initiated in diurnal phase and this is interrupted by reasons such lack of light
or decreased of light intensity, results in a total restart of metabolic energy
mechanism. These interruptions or decrease of PAR radiation may be due to
changes in weather, such as air pollution or sudden cloud, as well as the use of
greenhouses that being a barrier which causes changes in the light beam and can
also accumulate substances that block the arrive of PAR radiation to the foliage
plants. i.e., in crops which begin its photosynthetic processes and are interrupted
by blockage or decreased of solar radiation due to cloudy, the plants must wait for
a recurrence of the initial conditions of radiation to restart the total process
because the plants do not continue its metabolism in the point where is stopped.
Therefore, this involves a long metabolic delay of many hours or even days, this
depend of the event length, which is reflected in a reduction of the creation and
repair of maintenance and production tissues.
The implementation of this technological innovation made by Lightbourn Metabolic
Engineering and Lightbourn Biochemical Model, diametrically change the situation
because when the clusters of selenium, titanium, nickel and polioxomolibdate are
applied with an amphiphilic colloids nutrition, they are directly positioned on the
chloroplast tilacoidic structures and this acting as absortors, storers and
interconverters in a intermolecular triple switch, that able to realize consecutive and
reversible monoelectrics reductions, schematized as shown in the following figures:
Photosynthetic Phenomena
Optimizing of 563 nm Monochromatic Beam to Optimized Induced
Photosynthesis
I1 = Ultraviolet radiation
I2 = Visible light
I3 = H+ induce the interconversion among the states 5, 6 and 7, the 5 state do not
absorbs in the visible region, the 6 state (yellow-green) absorbs in 401 nm (01), the
7 state absorbs in 563 nm (02) purple.
The (H+) controls the reversible interconversion between 8 and 9, in
response to ultraviolet (I1) and visible (I2) stimuli. The intramolecular triple switch
modulates the ratio between the two forms and the absorbance (O) of ⑨ through
of photoinduced protonic transfer, the truth table and the logical sequence of the
circuit shows as performed intramolecular communication.
ó1
TETRAHIAFULVALENE (TTF)
BIPINIDINIUM (BIPY)
ABSORBANCE
Low
Low
High
Low
High
Low
High
Low
Low
High
High
High
The fluorescence of Pyrazolina interval is high when the (H+) is low and
viceversa. The fluorescence of the derived antrcinic is high when (Se+) or (K+) is
high, the emission is low when the concentration of both is low. (Low = 0) (High =
1)
Rotaxane (2)
Nanoscaled incorporating a Ni (II) Tris-Bipyridine stopper and two Bipyridium
electroactive units. This unit is able to perform two consecutive monoelectric
reductions and reversible in the presence of Triethylenediamine solution.
Cited Literature
Ahamad P, Prasad MNV, 2012. Environmental Adaptations and Stress
Tolerance of Plants in the Era of Climate Change. Springer New York. 531p.
Allakhverdiev S I, Kreslavski V D, Klimov V V, Los D A, Carpentier R y
Mohanty P, 2008. Heat Stress: An Overview of Molecular Responses in
Photosynthesis. Photosynthesis Research. 98:541-550.
Bellard C, Bertelsmeier C, Leadley P, Thuiller W, Courchamp F, 2012.
Impacts of Climate Change on the Future of Biodiversity. Ecology Letters. 15:365377.
Björn L O, McKenzie R L, 2008. Ozone Depletion and the Effects of
Ultraviolet Radiation. In: Photobiology: The Science of Life and the Effects of
Ultraviolet Radiation. Björn L O. ISBN: 978-0-387-72654-0.
Bray E A, Bailey-Serres J, Werentilnyk E, 2000. Responses to Abiotic
Stresses. In: Biochemistry and Molecular Biology of Plants. Buchanan, B.,
Gruissem, W. y Jones, R. American Society of Plant Physiologists.
Carrasco-Ríos L, 2009. Efecto de la Radiación Ultravioleta-B en Plantas.
IDESIA (Chile). 27(3):59-76.
Carpentier
R,
2005.
Effect
of
High-Temperature
Stress
on
the
Photosynthetic Apparatus. In: handbook of Plant and Crop Stress. Second Edition.
Pessarakli M. ISBN 0-203.90987-9.
Castañeda-Ovando A, Pacheco-Hernandez Ma De L, Paez-Hernandez M
E, Rodriguez J A, Galan-Vidal C A, 2009. Chemical Studies of Anthocyanins: A
Review. Food Chemistry, 103:859-871.
Castilla P N, 2007. Invernaderos de Plastico. Tecnología y Manejo.
Ediciones Mundi-Prensa, 2a edición. Pp.41-55.
González E M, Jurado E, González E S, Aguirre C O, Jiménez J P,
Navar J, 2003. Cambio Climático Global: Origen y Consecuencias. Ciencia UANL.
6(3):377-386.
Guo J, Wang M-H, 2010. Ultraviolet A-Specific induction of Anthocyanin
Biosynthesis and PAL Expression in Tomato (Solanum lycopersicum L.). Plant
Growth Regul 62:1-8.
Guo J, Han W, Wang M-H, 2008. Ultraviolet and Environmental Stresses
Involved in the Induction and Regulation of Anthocyanin Biosynthesis: A Review.
African Journal of Biotechnology 7(25):4966-4972.
Hao G, Du X, Faxing Z, Renjiu S, Jianmei W, 2009. Role of Nitric Oxide in
UV-B-induced Activation of PAL and Stimulation of Flavonoid Biosynthesis in
Ginkgo biloba Callus. Plant Cell Tissue and Organ Culture 97: 175-185.
Hatier J-H B, Gould K S, 2009. Anthocyanin Function in Vegetative
Organs. In: Anthocyanins: Biosynthesis, Functions and Applications. Gould K,
Davies K and Winefield C. Pp: 1-18.
Hidema J, Taguchi T, Ono T, Teanishi M, Yamamoto K, Kumagai T,
2007. Increase in CPD Photolyase Activity Functions Effectively to Prevent Growth
Inhibition Caused by UVB Radiation. The Plant Journal 50:70-79.
Hollósy F, 2002. Effects of Ultraviolet Radiation on Plant Cells. Micron.
33:179-197.
IPCC (Intergovernmental Panel on Climate Change), 2007. Climate
Change 2007. Synthesis Report. ISBN 92-9169-322-7.
Jaakola L, Hohtola A, 2010. Effect of Latitude on Flavonoid Biosynthesis in
Plants. Plan, Cell and Environment 33:1239-1247.
Jasper P, Kangasjärvi J, 2010. Reactive Oxygen Species in Abiotic Stress
Signaling. Physiologia Plantarum. 138:405-413.
Katerova Z, Ivanov S, Mapelli S, Alexieva V, 2009. Phenols, Proline and
Low-Molecular Thiol Levels in Pea (Pisum sativum) Plants Respond Differently
Toward Prolonged Exposure to Ultraviolet-B and Ultraviolet-C Radiations. Acta
Physiology Plant 31:111-117.
León-Chan R G, 2012. Inducción de Antocianinas en Pimiento Morrón
(Capsicum annuum) por Efecto de la Radiación Ultravioleta. Tesis de Maestria.
Centro de Investigación en Alimentación y Desarrollo (CIAD). 101p.
Lev-Yadun S, Gould K S, 2009. Role of Anthocyanins in Plan Defence. In:
Anthocyanins: Biosynthesis, Functions and Applications. Gould K, Davies K and
Winefield C. Pp: 21-48
Ligthbourn G J, Griesbach R J, Novotny J A, Clevidence B A, Rao D D,
Stommel J R, 2008. Effects of Anthocyanin and Carotenoid Combinations on
Foliage and Immature Fruit Color of Capsicum annum L. Journal of Heredity 99:
105-111.
Lightbourn R L A, 2010. Sistema Lightbourn de Transformación ExitaciónDeexitación Fotoquímica para Orbitales Moleculares en Química de Gelatores
Orgánicos de Bajo Peso Molecular. Tesis Doctoral para el Grado de Doctor en
Filosofía, Especialidad en Biología Molecular. Corllins University,Urbana Illinois,
USA. Propiedad Intelectual de Bioteksa y Lightbourn Research.
Lightbourn R L A, 2011a. Temperature Plant Stress Management. ISBN
978-0-9833321-4-5.
Lightbourn R L A, 2011b. Descripción de la Innovación del Grupo Hyper.
In: Modelo Bioteksa de Gestión de Tecnología e Innovación I + D + i = 2i.
ISBN:978-0-9833321-7-6.
Lightbourn R L A, Garza A V, González G D, González G A, 2011. La
Posibilidad de lo Imposible. ISBN: 978-0-9833321-1-4. 253p.
Lightbourn R L A, León-Chan R G, Heredia J B, 2012. Factores
Bioclimáticos Críticos Incidentes en el Equilibrio Suelo, Planta, Agua, Atmósfera en
el Cultivo de Manzana (Mallus domestica Borkh). http://www.slideshare.net/
DrLIGHTBOURN/congreso-de-la-manzana noviembre142012.
Mahdavian K, Ghorbanli M y Kalantari K
M, 2008. The Effects of
Ultraviolet Radiation on the Contents of Chlorophyll, Flavonoid, Anthocyanin and
Proline in Capsicum annum L. Turk J Bot. 32: 25-33.
Mazid M, Khan TA, Mohammad F, 2011. Role of Secondary Metabolites in
Defense Mechanism of Plants. Biology and Medicine 3(2): 232-249.
Mitra R, Bhatia C R, 2008. Bioenergetic Cost of Heat Tolerance in Wheat
Crop. Current Science. 94(8):1049-1053.
Nilsen E T, Orcutt D M, 1996. Water Limitation. In: The physiology of
Plants Under Stress. Abiotic Factors. Nilsen E T and Orcutt D M. ISBN 0-47103512-6.
Oren-Shamir M, 2009. Does Anthocyanin Degradation Play a Significant
Role in Determining Pigment Concentration in Plants? Plant Science 177:310-316.
Paul N D, Moore J P, McPherson M, Lambourne C, Croft P, Heaton J C,
Wargent J J, 2012. Ecological Responses to UV Radiation: Interactions Between
the Biological Effects of UV on Plants and
on Associated Organism. Physiologia
Plantarum 145:565-581.
Prado F E, Rosa M, Prado C, Podazza G, Interdonato R, González J A,
Hilal M, 2012. UV-B Radiation, Its Effects and Defence Mechanism in Terrestrial
Plants. In: Environmental Adaptation and Stress Tolerance of Plants in the Era of
Climate Change. Ahmad P y Prasad M N V. ISBN:978-1-4614-0814-7.
Salisbury F B, Ross W C, 1994. Fisiología Vegetal, Cuarta Edición. Grupo
Editorial Iberoamérica, S.A. de C.V., México D.F.
Santarius K A, 1973. The Protective Effect of Sugars on Chloroplast
membranes During Temperature and Water Stress and its Relationship to Frost,
Dessication and Heat Resistance. Planta. 113:105-114.
Sarghein SH, Carapetian J, Khara J, 2008. Effects of UV-Radiation on
Photosynthetic Pigments and UV Absorbing Compounds in Capsicum longum L.
International Journal of Botany 4(4):486-490.
Singh S, Kumari R, Agrawal M, Bhushan A S, 2012. Differential
Response of Radish Plant to Supplemental Ultraviolet-B Radiation under Varying
NPK Levels: Chlorophyll Fluorescence, Gas Exchange and Antioxidants.
Physiologia Plantarum 145:474-484.
Smith W K, Gao W, Steltzer H, 2009. Current and Future Impacts of
Ultraviolet Radiation on the Terrestrial Carbon Balance. Front. Earth Sci. China
3(1):34-41.
Steyn W J, 2009. Prevalence and Functions of Anthocyanins in Fruits. In:
Anthocyanins: Biosynthesis, Functions and Applications. Gould K, Davies K and
Winefield C. Pp: 89-105
Süss K H, Yordanov I T, 1986. Biosynthetic Cause of in vivo Acquired
Thermotolerance of Photosynthetic Light Reactions and Metabolic Responses of
Chloroplasts to Heat Stress. Plant Physiology. 81:192-199.
Taiz L, Zeiger E, 1988. Photosynthesis: The Light Reactions. In: Plant
Physiology, Second Edition.
Taiz L, Zeiger E, 2002. Energy and Enzimes. In Plant Physiology, Third
Edition. Taiz L y Zeiger E. ISBN 0-87893-823-0.
The Royal Society, 2009. Reaping the Benefits: Science and the
Sustainable Intensification of Global Agriculture. London, UK: The Royal Society.
Tsukasa M, Miei S, Masaaki, S, 2000. Changes in PAL, DAHP Synathase
(DS-Co and DS-Mn) Activity During Anthocyanin Synthesis in Suspension Culture
of Fragaria ananassa. Plant Cell Tissue and Organ Culture 62:135-139.
Wahid A, Gelani S, Ashraf M, Foolad M R, 2007. Heat Tolerance in
Plants: An Overview. Environmental and Experimental Botany. 61:199-223.
Wargent J J, Jordan B R, 2013. From Ozone Depletion to Agriculture:
Understanding the Role of UV Radiation in Sustainable Crop Production. New
Phytologist. 197: 1058-1076.
Zepp R G, Callaghan T V, Erickson III D, 2007. Interactive Effects of
Ozone Depletion and Climate Change on Biogeochemicla Cycles. Photochemical
and Photobiological Science 6:286-300.
Źróbek-Sokolnik A, 2012. Temperature Stress and Responses of Plants.
In: Environmental Adaptations and Stress Tolerance of Plants in the Era of Climate
Change. Ahmad P and Prasad M N V. ISBN: 978-1-4614-0814-7.