general principles of biomineralization: biologically induced mineralization biologically induced...
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General principles of biomineralization: Biologically induced mineralization
Biologically induced mineralization involves the adventitious precipitation of inorganic minerals by reaction of extraneous ions with metabolic products extruded across or into the cell wall.
The mineral products are closely associated with the cell wall and crystallochemically heterogeneous.
Ca2+ + 2HCO3- CaCO3 + CO2 + H2O
Biologically induced magnetite nanoparticles
20 nm
Biologically controlled mineralization involves the specialized regulation of mineral deposition and results in functional materials with species-specific crystallochemical properties.
General principles: Biologically controlled mineralization
uniform particle sizes
well-defined structures and compositions
high levels of spatial organization
complex morphologies
controlled aggregation and texture
preferential crystallographic orientation
higher-order assembly
hierarchical structures
General principles: Site-directed biomineralization
H2O
Intercellular –in the spaces between closely packed cells
0.5 mm
Intracellular – bilayer lipid vesiclesenclosed compartments within the cell
Extracellular – on or within an insoluble macromolecular framework secreted outside the cell
calcified coral
eggshell formation
PhysiochemicalSpatialStructuralMorphologicalConstructional
General principles: Site requirements
Spatial delineation – physical boundary for size and shape control
Chemical regulation– for increasing ionic concentrations (ionic pumping)
Diffusion limited ion flow– for controlling solution composition
Organic surface – nucleation
General principles: Control mechanisms
Gene pool Bioenergetics Biochemical
Boundary-organized biomineralization
The delineation of biological environments is of key importance in boundary-organized biomineralization because it provides sites of controlled chemistry that are spatially defined.
Control functions:
spatial delineation – size, shape and organization of the mineral phase
diffusion limited ion flow – ionic activities, solution composition, supersaturation
mineral passivation – surface stabilization against dissolution and transformation ion accumulation and transport – supplying chemicals to remote intra- and
extracellular mineralization sites
mineral nucleation – regulating interfacial energies
mineral transportation – moving mineralized structures to new construction sites.
Boundary-organized biomineralization; coccolith calcification
Light-dependent uptake: some CO2 fixed by photosynthesis influence of light on calcification
Some calcification occurs in dark using stored metabolic energy.
2HCO3
-
Ca2+
CaCO3
CO2
SO42-
SO42-
Photosynthesis
2HCO3
-
Ca2+ Ca2+
HCO3
-
CO32-CO2 OH
-
H2O
Sugars
Polysaccharides
Golgi vesicle
Medium Cell
H+
Coccoliths
+ Ca2+
uniport
CA
symport
Chemical control of biomineralization
Solubility
The solubility (S) of an inorganic salt depends on the balance between lattice energy (L) and ion hydration (H) ion pairing (IP) and complexation (C) in aqueous solution.
GS = GL - (GH + GIP + GC)
Lattice substitutions are important in controlling the solubility of biological apatite
Undersaturated
[Ca ]2+
/M
HAP
FAP
Plaque fluid
Saliva
Supersaturated
pH
100
10
1
0.15 6 7
Fluoride and tooth decay
Chemical control of biomineralization: Solubility product
The solubility product is a critical factor in determining the thermodynamic limit for the onset of inorganic precipitation. When the solubility product is less than the activity product (AP) of a solution then precipitation will occur until Ksp = AP.
MnXm(solid) nM+(aq) + mX-
(aq)
Ksp = {M+}n . {X-}m
Problems
Complexation with biological ligands (citrate/oxo/hydroxy)
Covalent polymers (silica)
Crystal size heterogeneity - Ostwald ripening
Kinetic effects organic sheaths etc
Chemical control of biomineralization: Supersaturation
Supersaturation is a measure to what extent a solution is out of equilibrium and represents the thermodynamic driving force for inorganic precipitation.
Relative supersaturation, Absolute supersaturation
SR = AP/Ksp SA = (AP – Ksp)/Ksp
The difference in chemical potential between the supersaturated solution and a solution at equilibrium with the solid is related to SR by
= kT lnSR
Supersaturation is highly regulated in biology through the process of boundary-organized biomineralization.
Supersaturation control in spatial boundaries
Mn+
Mn+
M (n+1)+
MX
Matrix
X-
X-
Mn+
E1 E2
H2O H2O
MC
A+
A+
B-
B-
H+H
+
Direct mechanisms to increase S
ion pumping ( + redox)
ion complexation/decomplexation
enzymic regulation of anions carbonic anhydrase (HCO3
-) alkaline phosphatase (HPO4
2-)
Indirect mechanisms
ionic strength - Na+ and Cl- transport
water extrusion – silica deposition?.proton pumping – pH changes
Chemical control of biomineralization: Nucleation
Homogeneous nucleation
The free energy of formation of a spherical nucleus, GN, is given by the
difference between the surface (interfacial, I) and bulk (B) energies,
GN = GI - GB
GI = + 4r2
where = interfacial free energy per unit surface area, and GB = - 4r3 Gv
3 Vm
where Gv = per mole solid-liquid phase
change, and Vm () is the molar
(molecular) volume.
G
G N*
G I
G N
G B
rr*
r* = critical sizeGN
* = activation energy
GN* = 1632 r* = 2Vm
3(kTlnSR)2 Gv
Rate; JN = Aexp(-GN
*/kT)
Nucleation control in biomineralization
JN
A
B
CSR* SR
Heterogeneous
Homogeneous
JN
SR*
SR increase GN* decrease JN increase
GN* (lnSR)-2
Need to control over catastrophic nucleation rate in pure solution at SR
*
GN* 3
small reductions in can have a marked effect on JN and r*
External substrate (dust etc) reduces and hence increases JN at given value of SR.
Heterogeneous nucleation occurs at lower SR and under control if SR
* is not breached.
GN* and JN determined by and SR and
biologically controlled by organic matrices and the membrane regulation of concentration gradients.
Extraneous particles with equal (A), variable (B) nucleation efficiencies. (C) without extraneous particles).
Oriented nucleation (epitaxy)
A B C
(A) non-oriented, (B) mosaic with crystals aligned only perpendicular to the substrate, (C) iso-oriented array with 3-D crystallographic alignment.
Structural control in biomineralization involves the preferential nucleation of a specific crystal face or axis on the surface of an organic matrix.
Key concepts: molecular recognition, lattice matching, electrostatic, stereochemical and structural complementarity.
% mismatchCaCO3//KBr 3
CaCO3//NaI 1
CaCO3 //KCl -2
CaF2//NaBr 8
CaF2//NaCl 3
CaF2//KBr 21
Chemical control of biomineralization: Crystal growth
mass transport (diffusion-limited) very high values of SA (x = 0)
polynucleation (growth islands) high SA (x > 2)
layer-by-layer growth moderate SA (x = 1)
screw dislocation growth low SA (x = 2)
Bulk diffusion
Surface adsorption + dehydration2D
diffusion
1D KINK
Crystal growth and termination are dependent on the level of supersaturation and occur through surface-controlled processes (active sites). STEP
Rate of growth, JG = k (SA)x
k = rate constant, SA = absolute supersaturation
Active sites - kinks, steps
screw dislocation
A
B
C
Chemical control of biomineralization: Crystal growth inhibitors
Soluble additives bind at steps/kinks, inhibit growth, change composition, structure and form.
Time / h
pH
0 1 2
7.0
7.2
7.4
Mg2+
control
F-
apatite crystallization
Time / min
pH
5 15
7.0
7.5
8.0
control
10
calcite crystallization + coccolith polysaccharides
t= 0
t = 4 min
intercalation texture50 m
sea urchin
Chemical control of biomineralization: Crystal morphology
CaCO3
Crystal morphology (habit) is determined by the relative rates of growth of different crystal faces, with the slow growing surfaces
dominating the final form.
controlLi+
HPO42-
010
110
100
Σ s{hkl}. A{hkl} = minimum
[001]
[110]
[110]
Chemical control of biomineralization: Habit modification
Molecular-specific interactions: electrostatic, stereochemical and structural matching modify the surface energy or mechanism of growth, or both.
CaCO3 +[malonate]2-
CaCO3 + polyaspartate
Chemical control of biomineralization: Polymorphism
JN
S (amorph)
S (crystal)
Amorphous Crystal
Ksp
(crystal) Ksp
(amorph) X Activity product
periodic order
Ostwald-Lussac law of stages
Crystallization proceeds along a series of structures with decreasing solubility and increasing thermodynamic stability. The structure of the critical nucleus is an important factor in controlling the crystallization pathway.
disordered/hydrated
A
B
G
Solution(M+
(aq) + X-(aq))
Amorphous
GN(B)Gg(B)
+
GT1
GN(A) Gg(A)+
GT2
GT3
Final mineral (crystalline)
The chemical control of crystallization pathways that involve a sequence of kinetic inhibition and phase transformation can result in a high degree of selectivity in crystal structure and composition.
Polymorphism and phase transformations
Accelerators and inhibitors
CALCIUM CARBONATE CALCIUM PHOSPHATE
Amorphous CaCO3
Vaterite
Aragonite
Calcite
Amorphous CaP
Brushite
Octacalcium phosphate
Hydroxyapatite
amorphous silica - biologically stable
Phase transformations - examples
Calcium phosphate
slow transformations of amorphous phase
octacalcium phosphate to hydroxyapatite
in situ solid state hydrolytic transformationx1 OCP (d100 = 1.868 nm) x2 HAP (2d100 = 1.632 nm
Calcium carbonate
fast transformations of amorphous phase unless stabilized by organic sheaths
high Mg2+ level in ACC high Mg calcites (30 mol%)
eg. sea urchin spicules
CDL
OEOCP
HAP
Traces of OCP precursor are left as a central dark linein enamel HAP crystals.
Larval sea urchin spicule - early growth stage
1m
Phase transformations - iron oxides
Solid state transformationpH 7, 80 C
Dissolution Reductive dissolution
RapidSlow-low Fe-low O2
-[H] agents-complexation
-Fe2O3
FERRITINFe2O3·nH2O
FeIII(aq) + FeII
(aq)Magnetite
Amorphous Ferrihydrite Goethite
FeIII
FeIII
O
OH
OH
+ FeII OH+(aq)
FeIII
FeIII
O
O
O
FeII + H+ + H2O
Fe3O4 + H+ + H2O
[FeIIIFeII(O)x(OH)y]n+
ferrihydrite magnetite (bacteria, chitons)
-10.0 -5.0 0.0 5.0 10.0
0.85
0.90
0.95
1.00
A1
A2C
B
Velocity (mm/sec)
Inte
nsi
ty
57Fe Mössbauer