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University of Groningen
Mechanisms in iron, nickel, and manganese, catalysis with small molecule oxidantsPadamati, Sandeep
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Chapter 1 Activation of NaOCl by transition metal complexes
Abstract NaOCl is a widely used oxidant, which is synthesized by passing electrochemically
generated Cl2 through cold alkali. The speciation of NaOCl is highly pH dependent and -
generally oxidizes substrates rapidly, which in turn limits the selectivity and specificity
that can be achieved in such reactions. Despite this, nature generates hypochlorite
enzymatically, either through oxygen activation to form Fe(III)-OOH or Fe(IV)=O species,
which further react with Cl- to give hypochlorite. The hypochlorite formed is used
further for selective oxidation or halogenation of the substrates. In this chapter, we
review briefly the chemistry of NaOCl and halogenases/haloperoxidases followed by a
review of biomimetic metal complexes that have been applied to control the reactivity
of NaOCl and achieve selectivity in oxidation or halogenation of substrates. Complexes
of manganese, iron and nickel, have seen most application and it is clear that control of
acidity is critical to the reactivity achieved and species formed, in particular high valent
intermediates and in the latter sections attention is turned to their study.
Sandeep K. Padamati, Apparao Draksharapu, Wesley R. Browne to be submitted.
1
Chapter 1
1.1 Introduction Sodium hypochlorite (NaOCl or bleach) is viewed as a ‘strong oxidant’ in colloquially,
primarily due to its reactivity in comparison to other oxidants such as H2O2 or O2 rather
than for thermodynamic reasons. It is used widely as a cheap and readily available
aqueous bleach, primarily due to the ease of its production, handling and storage, and
because the by-product it forms is predominantly NaCl. The use of hypochlorite,
domestically and medically, as a disinfectant has become widespread ever since the
development of moderately efficient methods of production in the 1900s. The
production of hypochlorite is a major industrial activity, carried out primarily using the
chloro alkali process developed by E. S. Smith in the late 1800s, in which brine is
electrolyzed to produce sodium hydroxide and gaseous chlorine which are then mixed to
form alkaline solutions of NaOCl.1 The Hooker process is used currently in which chlorine
is passed into cold aqueous sodium hydroxide (the low temperature is necessary to
reduce formation of chlorate). From a synthetic perspective, the primary detractors in
using NaOCl is that commercial NaOCl is supplied as an aqueous solution, which in turn,
limits its application to systems that are insensitive to water and its relatively wide
substrate scope. The taming of such a versatile and powerful oxidant presents many
challenges in comparison with the isoelectronic oxidant H2O2, not least due to the orders
of magnitude higher rate constants for its direct reaction with organic substrates. In this
chapter the first steps towards the use of transition metal catalyst to direct the
oxidation chemistry of hypochlorite will be discussed with a focus on efforts to
characterize reactive intermediates and to achieve selectivity. However, before
discussing these aspects, it is pertinent first to review briefly the basic inorganic
chemistry of hypochlorite and the several enzymes in which chlorine chemistry is
important, specifically halogenases and haloperoxidases.
1.2 pH dependence of the chemistry of aqueous NaOCl
The chemistry of chlorine is dominated by pH dependent equilibria and especially com-
and disproportionation reactions between the six oxidation states that chlorine can
achieve from perchlorate to chloride.1 The Latimer diagram for chlorine2 and the
Pourbaix plot shown below (Scheme 1) highlight the complexity of the chemistry of
chlorine and the need to consider carefully the pH of solutions in which reactions
involving chlorine species occur.
Cl2 gas and NaOH are prepared industrially by electrolysis of NaCl and both are used in
the Hooker process, currently in which chlorine gas is passed into cold aqueous sodium
hydroxide (the low temperature is necessary to prevent formation of chlorate).3
However, this reaction leads to many side products and additional reactions meaning
that commercially available sources of hypochlorite are contaminated with other species
such as perchlorate.1
2
Introduction
In the context of the present chapter NaOCl, in which chlorine has the formal oxidation
state of +1, pH dependent comproportionation and disproportionation reactions are of
interest, which can be deduced from the Latimer diagrams shown below.
Scheme 1 Latimer diagrams for chlorine under (a) acidic (pH 0), and (b) basic (pH 14) conditions.
Figure 1 Percentages of active chlorine species as a function of pH.1
At pH < 4 Cl2 gas is the dominant species present in terms of thermodynamical stability,
however, at pH 5 the major species is HClO, and at pH > 7 it is ClO-. The pH dependence
of the redox potentials relevant to these species is indicated in the Pourbaix plot below
for hypochlorite species, which shows that at all pH values hypochlorite is able to oxidize
water and the pKa for HOCl/OCl- is ca. 7.5.
Figure 2 Pourbaix diagram of hypochlorites in the chlorine-water system.1
In the Hooker process, mentioned above, chlorine gas is passed into cold aqueous
sodium hydroxide (equations 4 to 6 below). The yields of NaOCl depend critically on the
3
Chapter 1
pH as both it and HOCl undergo a complex set of reactions in solution (Scheme 2,
equations 5, 7-10) to form other chlorinated compounds and O2 (equations 7, 9, 10),
which is problematic industrially.1
Scheme 2 Reactions occurring in the production of NaOCl.1
1.3 Reactivity of NaOCl with alkanes, alkenes, and alcohols, and the
effect of acids The reactivity of NaOCl with organic substrates is well established and indeed there are
numerous reports of its use especially in the oxidation of alkenes to epoxides. Although
the focus of this chapter is on efforts towards metal catalyzed reactions with NaOCl, a
brief survey of the non-metal catalyzed reactions and their possible mechanisms in the
oxidation or chlorination of organic substrates will be made.
Scheme 3 Reactions of NaOCl at low pH condition.
The pH dependent chemistry of chlorine reagents means that with aqueous NaOCl, pH
control is essential. The equilibrium composition of NaOCl (aq) is pH-dependent (Scheme
3,), and under alkaline conditions (pH > 7), OCl- is the dominant species present and is
relatively stable (hence commercial hypochlorite bleach is sold as alkaline solutions). The
insolubility of NaOCl in organic solvents, however, presents practical problems in the
oxidation of organic substrates and hence phase transfer catalysts are required with two
4
Introduction
phase reactions (vide infra). Below pH 7 HOCl, is the significant form, which is soluble in
polar organic solvents such as CH2Cl2 circumventing the need for phase-transfer
catalysts in two phase reactions in the pH range 4-7. Below pH 4, Cl2 is a major
component of the aqueous hypochlorite solutions, and its reactivity will dominate the
organic oxidations performed.4
1.3.1 Oxidation of alkanes under acidic conditions
The oxidations of alkanes with hypochlorite is typically catalyzed by metal ions, vide
infra, however, acid catalyzed reactions have been reported, typically with acetic acid, in
which the reaction is likely to proceed through a radical pathway involving hypochlorous
acid formed in-situ. Hypochlorous acid, present in equilibrium with dichlorine monoxide
and water decays to form chloride and chlorine oxide radicals.5 Chlorine oxide radicals
chlorinate alkanes (Scheme 4).
Scheme 4 Proposed mechanism for acid catalyzed reactions with hypochlorite.5,6
Although of limited synthetic use as an alkane oxidant, an example of the use of bleach
for soil remediation is in the recent report by Chaouki and co-workers in the oxidation of
aliphatic petroleum contaminants (C10-C50) in a calcareous soil (average 5473 ppm C10-
C50, 15 wt% Ca).7 In this approach, decontamination was improved by using CO2 for
acidification to boost the oxidation with NaOCl and desorbing organic matter. It should
be noted that the reactivity may be affected strongly by the presence of transition
metals, such as manganese, although this was not investigated.
1.3.2 Oxidation of Alkenes
Alkenes, enones, and in particular chalcones, react readily with NaOCl to yield epoxides
(Scheme 5). The epoxidation of alkenes is typically highly pH dependent, not least due to
subsequent epoxide ring opening reactions and alkene chlorination reactions, to yield,
e.g., halohydrans.8 Typically the ClO• radical is invoked as the reactive species due to the
occurrence of hydrocarbon chlorination (vide supra), and from Hammett ρ values for the
chlorination of toluene.5
5
Chapter 1
Scheme 5 Epoxidation of enones at pH 8 - 8.5 with NaOCl.3
The enantioselective epoxidation of α,β-unsaturated ketones using NaOCl as the
terminal oxidant can be accomplished with high selectivity through the use of chiral
phase transfer catalysts (PTCs).9
1.3.3 Oxidation of alcohols
The oxidation of secondary alcohols to ketones with solutions of NaOCl10 proceeds
relatively cleanly with added acetic acid (Scheme 6).11 Excess hypochlorite is quenched
with sodium bisulfite, and essentially pure ketone is obtained simply by extraction of the
product into dichloromethane or ether, thus providing a convenient approach to highly
selective oxidation of secondary alcohols in the presence of primary alcohols,12 and
without epimerization of alcohols bearing β-stereocenters (Scheme 6). Kinetic studies
indicate that Cl2 is the active oxidant at the low pH in which these reactions are
performed.13 A detailed review of the oxidation of aldehydes and nitriles with NaOCl is
given elsewhere.4
Scheme 6 Oxidation of secondary alcohols to ketones with NaOCl and acetic acid.4
1.3.4 Phase transfer catalyzed reactions
The insolubility of NaOCl in organic solvents has prompted the use of phase transfer
catalysts (typically tetraalkyl ammonium salts) in reactions carried out at pH > 8. Lee and
co-workers have proposed that the PTC – OCl- ion pair partitions into the organic layer.14
In the absence of the PTC, little if any oxidation is observed, consistent with the absence
of significant interfacial reactivity. The ion pair shows increased reactivity in the organic
phases enabling clean and rapid oxidation, with the products recovered by phase
separation and solvent stripping.
The mechanistic study of these reactions was considered by Hossein and co-workers in
the study of the oxidation of various hydrocarbons with NaOCl, together with a phase-
transfer catalyst (PTC).5 They concluded that a free-radical mechanism was involved
rather than an electrophilic or heterolytic mechanism, since both light and oxygen affect
6
Introduction
the rate of reaction and product distribution, the product distribution with alkyl
aromatics and alkenes was typical of radical reactions and the relative reactivity of
primary, secondary, and tertiary C-H groups was as expected for a radical mechanism.
Furthermore azaphenanthrenes were converted to epoxides rather than the
corresponding N-oxides.15 Hence ClO• is likely to be the reactive reagent in the NaOCl-
PTC system, with its formation possible via the reactions shown in Scheme 7.
Scheme 7 Proposed reactions for the formation of ClO• under alkaline PTC conditions.5
It is notable that the NaOCl-PTC system does not show product distributions expected
for reactions involving chloride radicals, and hence the reaction of chloride radicals with
hypochlorite is efficient as well as being thermodynamically more favored. Hence the
oxidation of alkanes, alkenes and chlorination of anisoles were proposed to follow the
mechanisms shown in the Scheme 8.
Scheme 8 Proposed mechanisms for oxidation and chlorination of (a) alkenes, (b)
alkanes and (c) anisoles by NaOCl-PTC.5
For the reactions to proceed efficiently the concentration of Cl2O (for pathways b and c)
and ClO⁻ (for pathway a) should be constant in order to consume Cl• and regenerate
ClO•. Hence, a PTC will not only increase the concentration of ClO⁻ in the organic phase
but also increase the rate of mass transfer between the phases.16 Furthermore, the PTC
will stabilize the hydroxide ions formed in these reactions and remove them to the
aqueous phase efficiently. The observation that oxidation of azaphenanthrene (7,8-
benzoquinoline) in a two-phase reaction results in a mixture of the N-oxide and epoxide
products, whereas only the N-oxide is formed under single phase conditions, indicates
7
Chapter 1
that the mechanisms proceeding in the two-phase reactions are distinct from those
(possibly electrophilic) mechanisms occurring in aqueous solutions.15
1.4 Halogenases and haloperoxidases Halocarbons are common motifs in marine natural products, such as antibiotics,
hormones of pharmaceutical interest, agrichemicals, and are key reagents in organic
synthesis.17 Current methods for the late stage halogenation of complex compounds
present challenges as great as the corresponding challenges in late stage hydroxylation
of C-H bonds, with the reactivity needed to cleave a C-H bond incompatible with many
functional groups. Despite these challenges, nature has hijacked peroxidases and
oxygenases to achieve late stage halogenation with excellent selectivity and
specificity.18,19 A number of structures of haloperoxidases have been reported already20
and they are classified based on the nature of the terminal oxidant used into
haloperoxidases and halogenases.18 Vanadium and heme dependent enzymes employ
H2O2 to generate the reactive intermediates needed for C-H halogenations and are
classified as haloperoxidases. Non-heme and flavin dependent enzymes that use O2 by
contrast are referred to as halogenases.
I.4.1 Halogenases
1.4.1.1 Flavin dependent halogenases
The class of halogenases that require a flavin cofactor, such as PrnA (tryptophan 7-
halogenase) and PrnC, are not dependent on transition metal ions and engage in highly
regiospecific chlorination reactions. The high specificity precludes involvement of
HOCl/OCl- and points towards the generation of X+ (X = Cl or Br) equivalents to
halogenate electron rich substrates.
Scheme 9 Mechanistic proposal for the formation of dichloropyrrolyl-S-PltL. A proposed FAD-4α -OCl intermediate is formed from the attack of Cl- on FAD-4 α -OOH. The FAD-4 α
-OCl intermediate then reacts with substrate pyrrolyl-S-PltL in a two-electron electrophilic aromatic substitution to first form the 5-chloropyrrolyl intermediate and
then the 4,5-dichloropyrrolyl product.22(b)
Van Pée and co-workers have proposed the involvement of a 4α-hydroperoxy flavin
intermediate, which epoxidize alkenes and incorporate halogens regioselectively as
8
Introduction
halohydrins followed by removal of water to form the final chlorinated product.21 Walsh
and co-workers have proposed a FAD-4α-OCl intermediate,22 generated by reaction of
FADH2 with O2 and Cl to form an O-Cl intermediate in the active site which then reacts
with substrates (via electrophilic aromatic substitution) to yield chlorinated products
(Scheme 9). An alternative mechanism proposed by Naismith and co-workers23 was
based on the crystal structure of PrnA (with FAD, tryptophan and chloride bound).
Scheme 10 Mechanism for halogenation by Flavin dependent haloperoxidases proposed by Naismith and co-workers (formation of HOCl is followed by protein mediated
electrophilic aromatic substitution).18,24
Overall the halogenation involves HOCl equivalents, produced by reaction of Cl- anions
with the FAD-OOH intermediate formed by reaction of FADH2 with O2. However, the FAD
cofactor provides control of its reactivity by holding it within the active site through H-
bonding (Scheme 10).24,25
1.4.1.2 Non-heme iron dependent halogenases
Iron dependent halogenases, such as SyrB1 and CmaA, use non-heme Fe(II)/α-
ketoglutarate with O2 for halogenation of the inert aliphatic C-H bonds (Scheme 11).18,26
These enzymes are related to oxygenases based on a non-heme Fe(II)/αKG active site
except that a chlorido ligand replaces an aspartate moiety,18,26 and contrast with flavin
dependent enzymes in that they use chloride anions rather than Cl+ equivalents. The
general mode of action of this class of enzyme involves binding of a substrate within the
active site close to an Fe(II) center which facilitates dissociation of an aqua ligand and
coordination of O2 to form an Fe(III)-OOH intermediate and, through O-O bond cleavage
coupled with a decarboxylation, to form an Fe(IV)=O species. The later species has been
identified by Mössbauer and (resonance)Raman spectroscopy. Reaction of the Fe(IV)=O
intermediate with a C-H group in the substrate yields a Cl-Fe(III)-OH intermediate and an
alkyl radical, followed by formal reaction of a chlorine radical (Cl•) with the alkyl radical
(R-CH2•) to form the C-Cl bond.26 Although attack by a hydroxyl radical can compete with
chloride radicals, this pathway is less thermodynamically favourable.20d,27
9
Chapter 1
Scheme 11 Proposed mode of action of Fe(II) and αKG-dependent halogenases. R =
CH2-L-CH(NH2)-CO-S-CytC2; R’ = (CH2)2CO2.26
1.4.2 Haloperoxidases
1.4.2.1 Vanadium dependent haloperoxidases
Vanadium bromo peroxidase is one of the better known haloperoxidases owing to its
likely involvement in the biosynthesis of several halogenated natural products.28 In these
enzymes the vanadium ion is coordinated by histidine residue’s imidazole,18 and is able
to halogenate electron rich substrates using a combination of H2O2 and X- (where X- = Cl-,
Br- and I-), Scheme 12.29 Formation of a side on vanadium peroxy species is followed by
two electron oxidation of a halide to form V-O-X. Although the details of the mechanism
by which the vanadium dependent haloperoxidases halogenate substrates remain
unclear, it is generally accepted that they produce X+ (X = Cl, Br and I) equivalents, which
further halogenates electron rich substrates.
10
Introduction
Scheme 12 Formation of hypochlorite intermediate in vanadium-dependent haloperoxidases.18
1.4.2.2 Heme dependent haloperoxidases
As with the vanadium dependent haloperoxidases, heme dependent haloperoxidases
use a combination of H2O2 and halide ions (Scheme 13). A few examples of heme
dependent haloperoxidases are chloroperoxidase (CPO),30 myeloperoxidase (MPO),
thyroid peroxidase (TPO), lactoperoxidase (LPO) and eosinophil peroxidase (EPO), and as
with flavin dependent halogenase, they generate X+ (X = Cl or Br) equivalents and
therefore halogenate electron rich substrates. Reaction of heme Fe(III) with H2O2 leads
to formation of an Fe(IV)=O species, the so called Compound I.31,32 Inner sphere two
electron oxidation of a halide ion by Compound I yields heme-Fe(III)-O-X (where X = Cl,
Br and I),32 and hence a Fe(III) hypohalite species is proposed to engage in substrate
halogenation.
Scheme 13 Proposed mechanism in heme-dependent halogenation reactions.18
Direct spectroscopic evidence for a heme-Fe(III)-OCl adduct in heme dependent
haloperoxidases is thus far elusive, with only the observation of a heme-Fe(III)-OCl
adduct made recently by Fujii and co-workers.33 Reaction of OCl- with [(TPFP)Fe(III)(OH)]
in CH3CN/CH2Cl2 generated an intermediate assigned as [(TPFP)Fe(III)(OCl)2]-, that was
stable for 1 h at -60 °C, decomposing to [(TPFP)Fe(IV)(O)]. Indeed, only recently was a
non-heme Fe(III)-OCl reported by Draksharapu et al. at room temperature under
biological relevant conditions (vide infra).34 The transient nature of such species and the
potential to tame the reactivity of, especially OCl-, has prompted recent efforts in the
exploration of biomimetic complexes.
1.5 Reaction of biomimetic metal complexes with NaOCl Despite that it is isoelectronic with H2O2, the reactivity of metal complexes with
HOCl/NaOCl has received little attention primarily due to its intrinsic reactivity with
organic substrate. Nevertheless, recently the number of reports dealing with this topic
has increased with attention focused on manganese, iron and nickel complexes
primarily, in particular those bearing porphyrin ligands.35 In this section, the systems
reported with each metal will be discussed in turn.
11
Chapter 1
1.5.1 Manganese based complexes
1.5.1.1 Manganese porphyrins
Tabushi et al. reported the reactivity of manganese porphyrin complexes with NaOCl
over two decades ago in the context of generating intermediates relevant to the water
oxidation center of PSII,36,37 and noted that the combination could be used to oxidize
benzyl alcohol to benzaldehyde. Meunier et al. reported, as early as 1984, the use of
manganese porphyrin complexes with NaOCl in the epoxidation of olefins.38 These early
reports highlighted the need for PTCs, as styrene conversion to its epoxide was
negligible in the absence of PTCs. Furthermore, control of pH is essential as mentioned
above at low pH uncatalyzed oxidation to halohydrins and allylic chlorination is
observed.39 A key aspect of porphyrin chemistry is the involvement of proximal ligands
(such as pyridine ligand), Indeed, pyridine coordination to manganese centers was
accompanied by an increase in catalytic activity. Furthermore, increase in OCl-
concentration in the organic phase due to the PTCs leads to the formation of a Mn(III)-
OCl species, followed by heterolytic O-Cl bond cleavage to generate a reactive Mn(V)=O
species, which further reacts with 3-carene. The formation of -epoxide from 3-carene
in the presence of the catalyst, in contrast to the formation of -epoxide by the
uncatalyzed reaction supports this mechanism (Scheme 14).
Scheme 14. Formation of -epoxide of 3-carene by using Mn(TPP)OAc and NaOCl.38
Saturation kinetics were reported by Collman et al. for the epoxidation of various olefins
(styrene, cyclic olefins, or aliphatic alkenes) with Mn(TPP)Cl or Mn(TMP)Cl (where TPP
(meso-tetraphenylporphyrinato) and TMP (meso-tetramesitylporphyrinato) and 4'-
(imidazol-1-yl) acetophenone as axial ligand (Scheme 15).40 The data obtained was
consistent with the mechanism proposed by Tabushi et al.(vide supra).
12
Introduction
Scheme 15 Proposed catalytic cycle for olefin epoxidations by "OCl-/Mn(Porphyrin)Cl/L” where L is an axial ligand.40a
The intermediacy of the Mn(III)-OCl species was more recently supported by similar
species in the oxidation and chlorination of C-H bonds proposed by Groves and co-
workers.41 They proposed a mechanism in which formation of a LMn(IV)-OH or a
O=Mn(V)=O species occurred prior to substrate oxidation.42 Following hydrogen atom
abstraction the alkyl radical forms the product by chlorine atom transfer from L-Mn(IV)-
OCl to regenerate the O=Mn(V)=O species. In order for the chain reaction to proceed,
alkyl radical has to diffuse out of the [O=Mn(IV)-OH •R] cage, and the rearrangements
observed in the chlorination of norcarane indicate that this occurs (Scheme 16).
Scheme 16 Proposed C-H chlorination mechanism.41
1.5.1.2 Manganese salen complexes
The synthetic accessibility of salen complexes together with their similarity (in terms of
planar coordination) with porphyrins has prompted considerable interest in their
complexes over the last decades. Manganese salen complexes have been applied widely
in alkene epoxidations, most notably by Kochi,43 Jacobsen and co-workers. Jacobsen and
co-workers reported the use of Mn-salen complexes in epoxidations with NaOCl,44 and
considerable effort has been directed towards comparing the reactivity of Mn-salen
13
Chapter 1
complexes with a broad range of oxidants, such as PhIO, m-CPBA.45 Several mechanisms
have been proposed for the mode of action of Mn-salen complexes with NaOCl based on
species observed, product distributions and the effect of pyridines on catalytic activity,
and have raised key questions, in regard to catalyst degradation, and of phase transfer
agents in increasing reactivity and selectivity.
Reider and co-workers,46 reported the 4-(3-phenylpropyl)pyridine N-oxide (P3NO) as an
axial ligand to achieve higher yield, and enantioselectivity in the asymmetric epoxidation
of indene using aqueous NaOCl, catalyzed by Jacobsen’s chiral manganese salen
complex. It was proposed that P3NO increased the rate of mass transfer of HOCl to the
organic layer, where HOCl oxidizes Mn(III) to Mn(V)=O, which forms the rate limiting
step in the reaction based on kinetic data, which show that the rate of epoxidation is
independent of indene concentration but is dependent on the concentration of HOCl.
Furthermore, control of the concentration of OCl- in the organic layer and the
observation that the rate of oxidation of a redox indicator, diphenylbenzidine, resembles
the rate of epoxidation support this conclusion. Nevertheless mass transfer (e.g., stirring
speed) effects in the two phase system in the absence of axial ligand indicate that
oxidation can occur in the interfacial region. Thus, the axial ligand is proposed to play at
least two roles in the epoxidation of indene: it stabilizes the catalyst, presumably by
ligation, and it increases the epoxidation reaction rate by drawing the active oxidant,
HOCl, into the organic layer.46
Polymeric catalysts are also one of the ways to improve the catalytic efficiency. Many
groups have reported the use of polymeric Mn(III)-salen complexes to give high yields
and selectivity in the oxidation of alkenes using NaOCl as oxidant.47,53 Jasra and co-
workers has reported polymer immobilized chiral Mn(III)-salen complexes prepared
from 1S,2S-(+)-1,2-diaminocyclohexane, and 1R,2R-(+)-l,2-diphenyl ethylenediamine
with 5,5-methylene-di-3-tert-butylsalicylaldehyde.48 These complexes provided the
enantioselective epoxidation of styrene, indene and chromenes in presence of pyridine-
N-oxide (PyNO) as an axial base and NaOCl as oxidant and were recycled several times.
The polymeric Mn(III)-salen complexes used in the present study can be easily separated
from the reaction system and reused effectively.
Although several mechanisms have been proposed to rationalize the chemistry of Mn-
salen complexes with NaOCl, it is generally accepted that the initial step is the formation
of a Mn(III)-OCl intermediate that undergoes heterolytic O-Cl bond cleavage to liberate
Cl- and form a Mn(V)=O species. The latter intermediate is believed to be responsible for
the oxidation of alkenes (Scheme 17).46,49 This mechanism is essentially analogous to the
mechanisms proposed for the structurally related Mn-pophyrin complexes (vide supra).
14
Introduction
Scheme 17 Proposed mechanism for oxidation of alkenes with manganese salen complexes.45
A key challenge in mechanistic studies is the identification of reactive intermediates and
several intermediates were proposed to form upon reaction of Mn-salens with PhIO,
mCPBA, and NaOCl (Chart 1).
Chart 1 Intermediates proposed to be involved in catalytic cycles.45
Recent evidence for multiple oxidants or oxidation pathways in these (Mn(salen))
reactions has challenged the paradigm of a common mechanism with the formation of
adducts between the terminal oxidants and Mn(salen) species proposed to compete
with O=Mn(V)-(salen) as oxygen transfer agents. Seebach and co-workers have proposed
that with oxidants such as NaOCl, XO-Mn(III)(salen) species are involved in a concerted
pathway in the oxidation of substrates. In contrast with oxidants such as PhIO,
O=Mn(V)(salen) species lead to formation of radical intermediates and thereby affect
the trans/cis-epoxide ratio (i.e. loss of stereochemistry).50 Brauman and co-workers have
proposed that oxidants such as PhIO lead to a mixture of PhIO-Mn(III)(salen) adducts
and O=Mn(V)(salen), and the data supports the opposite mechanisms (Seebach and co-
workers) for these two types of species.51 Radical trapping and free energy studies show
a nonlinear Eyring plot for PhIO, while with mCPBA and NaOCl the corresponding plots
are linear, consistent with a single oxidant, O=Mn(V)(salen), in the latter cases. Further
15
Chapter 1
support for this conclusion is the lower levels of trans-epoxide obtained from cis-alkenes
(stilbene) with NaOCl.45
1.5.2 Iron complexes as models for halogenases and haloperoxidases Iron dependent halogenases and haloperoxidases play a key role in halogenation
reactions in nature (vide supra). Bio-mimetic complexes can provide insight into the
mechanisms by which these enzymes operate and open opportunities for novel catalytic
reactivity. In the case of halogenases, the reaction of H2O2 with the Fe(II) center leads to
formation of an Fe(IV)=O species with a porphyrin π-cation radical ligand (compound
I).52 Reaction of compound I with chloride results in the formation of an Fe(III)-OCl
species transiently, which releases OCl-.33 Such Fe-OCl species have been proposed as
key intermediates in catalytic oxygenation reactions and hence their formation is of
substantial wider interest.50,53
Despite that the formation of a putative Fe(III)-OCl species rationalizes the reactivity
observed, its direct detection has not been achieved for enzymatic systems and hence
generation of such species in model complexes is of interest.54,33 Alexander and co-
workers proposed the formation of an Fe(III)-OCl species during the oxidation of alkanes
with NaOCl and Fe(III) tetramesityl-porphyrin chloride (TMPFeCl).55 Under basic
conditions, the 3/1 alcohol/ketone ratio was obtained with a remarkably high KIE
observed.
Hypochlorito iron(III) porphyrin complexes have received relatively little attention in
comparison with those species formed from other terminal oxidants such as H2O2 or
iodosylarene.56,41 Recently, Cong and co-workers reported the spectroscopic
characterization of an intermediate species assigned the structure TPFPFe(III)-(OCl)2
(where TPFP is 5,10,15,20- tetrakis(pentafluorophenyl)porphyrinat), formed during the
reaction of (TPFP)Fe(III)-OH with TBAOCl (tetrabutyl ammonium hypochlorite), which
reacted with thioanisole to give (TPFP)Fe(III)-Cl and (TPFP)Fe(III)-OH. TPFPFe(III)-(OCl)2
reacted with cyclohexene to form a transient TPFP Fe(IV)=O and also showed reactivity
in sulfoxidations, chlorinations, and epoxidations.33
In contrast to heme systems, relatively little attention has been given to non-heme iron
complexes reactivity with NaOCl. Balland and co-workers noted the appearance of a
transient intermediate with absorbance maximum at 440 nm when generating a non-
heme Fe(IV)=O species from the corresponding Fe(II) L(L= N-methyl-N,N’,N’-tris(2-
pyridylmethyl)propane-1,3-diamine) with NaOCl, which they tentatively assigned as
Fe(II)-OCl intermediate.57
The first non-heme Fe(III)-OCl species was characterized spectroscopically by
Draksharapu et al. recently.34 Addition of near stoichiometric NaOCl to
[Fe(II)(Cl)(MeN4Py)]2+ (where MeN4Py = 1,1-di(pyridin-2-yl)-N,N-bis(pyridin-2-
ylmethyl)ethanamine) under acidic conditions (pH 2-5) resulted in formation of
16
Introduction
[Fe(III)(OCl)(MeN4Py)]2+, which undergoes homolysis of the OCl bond to yield
[Fe(IV)(O)(MeN4Py)]2+.34 The non heme Fe(III)-OCl intermediate is stable at room
temperature and shows a weak visible absorption band (max 480 nm), resonantly
enhanced Raman bands (580, 653, and 673 cm-1), and an EPR spectrum characteristic of
a mononuclear S = ½ Fe(III) complex (g = 2.26, 2.15, and 1.97).33 However, DFT
calculations indicate the formation of an intermediate Fe(II)-OCl species also, that
undergoes rapid heterolytic O-Cl bond to yield the corresponding Fe(IV)=O species
(Scheme 18). It is notable, in the context of iron dependent haloperoxidases, that the
Fe(IV)=O species reacts with Cl- to form an Fe(III)-OCl.
Scheme 18 The reaction mechanism for the formation of [Fe(III)(OCl)(MeN4Py)]2+ and [Fe(IV)(O)(MeN4Py)]2+ with the free energies (ΔG) calculated for each step. Reproduced
with permission from ref. 34. Copyright Wiley (2015).
Although the observation of Fe(III)-OCl species is still rare, Sen Gupta and co-workers
demonstrated the formation of Fe(V)=O complexes upon reaction of the corresponding
Biuret-amide-modified Fe(III)−TAML complex (where TAML is tetra amido macrocyclic
ligand) upon reaction with NaOCl. Reaction with 0.5 equiv. of NaOCl in CH3CN, resulted
in initial formation of a Fe(IV)2(μ-O) complex, with a second 0.5 equiv. of NaOCl
producing the Fe(V)=O species.58 Collins and co-workers have shown recently that Fe(III)-
TAML (beheaded) complexes show a pH dependence in their reaction with NaOCl
forming either Fe(V)=O and Fe(IV)=O species, at low and high pH, respectively (Scheme
19).59
17
Chapter 1
Scheme 19 pH-Dependent transformations of Fe-TAML species generated with NaOCl in water.59
Scheme 20 Oxidation of organic substrates with catalytic nickel(II) salts and aqueous bleach (a-d), and (e) proposed mechanism for the oxidation of 3-butenoic acid to
fumaric acid.62
Although nickel dependent enzymes are uncommon, there are some examples such as
Ni-SOD, and there has been some effort, especially recently, towards the study of Ni(II)
complexes as catalysts for organic oxidations with a wide range of oxidants including
bleach.
18
Introduction
1.5.3 Reactivity of Nickel complexes with HOCl/NaOCl
Interest in nickel complexes as oxidation catalysts with a wide range of oxidants has
increased, the use of simple nickel salts with NaOCl was already studied in the 1970s.
The reaction of stoichiometric nickel oxides and hydroxides60 with organic substrates
was well established for example Bekkum and coworkers noted that diol cleavage of
some sugars could be achieved with nickel oxides and bleach to yield carboxylic acids.61
It should be noted that reaction of bleach with nickel(II) salts leads to rapid formation of
nanoparticulate nickel oxides with high surface areas that are useful as heterogeneous
catalysts.62 Recently, Grill et al. have shown that NaOCl can be used synthetically with
catalytic amounts of nickel salts (ca. 2 mol%) such as nickel(II)acetate and
nickel(II)chloride in the oxidation of primary and secondary alcohols to ketones and
acids,and the epoxidation of α,β-unsaturated carboxylic acids (Scheme 20).62
1.5.3.1 Ni(II) salen complexes in oxidations with NaOCl
In the mid-1980s, Burrows and co-workers, and thereafter Kureshy and coworkers
demonstrated that cyclam and salen based nickel complexes catalyzed the epoxidation
of alkenes with NaOCl.63,64,65 In these studies the formation of a fine black suspension
during the reaction was noted indicating formation of NiO(OH)2.60,62 However, the
involvement of such inorganic particulate species in the oxidation was excluded as only
trace epoxidation was observed under the same conditions with Ni(II) acetate, and the
recovered black precipitate did not oxidize the substrate. Similar conclusions were
drawn later by Draksharapu et al. (vide infra).72
Scheme 21 Proposed mechanism for epoxidation of (E) and (Z)-stilbene with Ni(II) salen complexes and NaOCl.64
The formation of Ni(IV)-oxo intermediates were proposed for the cyclam catalysts with
PhIO and an analogous mechanism was proposed to occur with NaOCl (Scheme 21).
19
Chapter 1
Notably, the oxidation of olefins proceeded without stereospecificity, indicating the
formation of radical intermediates.64
Subsequently, Burrows and co-workers proposed a mechanism based on the effect of
pH and additives on the reaction.65 At pH 9.3, the rate of epoxidation was highest, which
indicated that at that pH, sufficient concentrations of chlorine monoxide, the proposed
terminal oxidant, formed (Scheme 22). Indeed the reaction of Cl2O with Mn(TPP)Cl and
with [Ni(CN)4]2- has been reported already, with [Ni(CN)4]2- reacting with Cl2O 107 times
faster than with HOCl. It was proposed that a NiIV(CN)4(Cl)(H2O)- intermediate formed.66
Scheme 22 Formation of Cl2O from HOCl.65
Oxidation of the Ni(II) salen complex to the Ni(III) state with Cl2O followed by exchange
of Cl- for OCl- and homolytic Ni(III)-OCl bond cleavage would generate ClO•, a known
epoxidizing reagent (Scheme 23).5,67
Scheme 23 Proposed mechanism for generation of ClO• (epoxidation) and Cl• (chlorination) with NiII complexes. Ligands are omitted for clarity.65
An alternative pathway involves the intermediacy of a LNiIII-oxo radical formed by
reaction with HOCl (equation 16) or by cleavage of the O-Cl bond (Scheme 24). The LNiIII-
O• formed could engage in H atom abstraction and epoxidation.68
20
Introduction
Scheme 24 Generation of salen NiIII ClO• species.65
Freire and co-workers69 noted that methyl substituents on the salen ligand on Ni-salen
complex did not affect selectivity trans-β-methyl styrene, however O2 increased
conversion prompting the proposition of two pathways; a mechanism in which a Ni-oxo
complex is generated by reaction with radical species formed from NaOCl in the
presence of O2, which leads to faster alkene conversion but not a change in selectivity,
analogous to the rebound mechanism proposed for Cytochrome P450.70 Recently, it has
been shown that short-lived radicals are not bound to metal complexes.71 In an
alternative mechanism, substrate binding to the metal oxo complex occurs lowering
conversion but increasing epoxide selectivity (Scheme 25).
Scheme 25 Mechanisms for the oxidation of trans-β-methyl styrene with NaOCl and Ni(II) (salen) complexes.69
1.5.3.2 Ni(II) triazacyclononane based catalysts for oxidations with NaOCl.
Recently Draksharapu et al. reported a Ni(II) catalyst based on the facial coordinating
triazacyclononane scaffold (PyTACN = 1-(2-pyridylmeth-yl)-4,7-dimethyl-1,4,7-
triazacyclononane) for the chlorination of alkanes with NaOCl as both oxidant and halide
transfer agent.72 Although activity under basic conditions was low, addition of acetic acid
21
Chapter 1
increased the rate of cyclohexane chlorination beyond that (marginally) of the
background reaction. The inhibition seen by simple Ni(II) salts, indicated that the
Ni(II)(PyTACN) complex was playing an active role in the reactions observed, and several
intermediates were characterized spectroscopically.
However, the KIE measured through a competition reaction between cyclohexane-H12
and cyclohexane-D12 was 2, which, together with the product distribution obtained with
cis-1,2-dimethylcyclohexane and decalins, is consistent with a highly reactive hydrogen
atom abstracting reagent, e.g., a chlorine radical. The increase in reaction rate (catalyzed
and non-catalyzed) upon addition of acetic acid, is expected given that under acidic
conditions HOCl forms ClO• species (vide supra), which was confirmed by the
appearance of an band at ca. 320 nm upon addition of acetic acid to NaOCl in
acetonitrile. Nevertheless despite that the role of the catalyst appeared to be to
accelerate the formation of the chlorine species responsible for substrate chlorination
(Scheme 4),5,73 several species of interest in the development of Ni(II) catalysts are
worth mentioning. A low spin Ni(III) species was observed (EPR signals at g⊥ = 2.13, and
g// = 2.03)74 with resonantly enhanced Raman bands at 724 cm-1 for Ni(III)-OH and 1682
cm-1 for a Ni(III)-OOCCH3 species. However, as with other Ni(III)-OR species reported
recently75 it is unlikely that these species are oxidants in the case of cyclohexane, as they
are only capable of undergoing hydrogen atom transfer (HAT) with weak O−H bonds.
Scheme 26 Proposed mechanism for C-H chlorination by Ni(II)-PyTACN complexes reaction.72
The mechanism proposed is shown in Scheme 26, in which [(L)Ni(II)-OCl(S)]+ (A) is
formed by reaction of Ni(II)PyTACN with NaOCl and subsequently decays to
[(L)Ni(III)−OH(S)]2+ (B) (where S is solvent), possibly through homolytic cleavage of the
O−Cl bond. This mechanism rationalizes the release of Cl• atoms. Notably, the hydrolysis
22
Introduction
of acetonitrile to acetic acid was observed resulting in the formation of [(L)Ni(III)-
OOCCH3 (S) ]2+(C), and thereafter [(L)Ni(II)-OOCCH3 (S)]2+(D), presumably via oxidation of
ClO2− to form ClO2. Coordination of NaOCl to [(L)Ni(II)-OOCCH3(S)]2+ (D) regenerates
[(L)Ni(III)-OH(S)]2+ (B) more rapidly than from the original complex. Acids, such as acetic
and triflic acid, increase the rate and extent of formation of [(L)Ni(III)-OH(S)]2+(B),
indicating proton acceleration of O−Cl homolytic cleavage. Ultimately, these reactions
generate Cl• atoms and ClO2 in a catalytic cycle in which the nickel complexes undergo a
Ni(II) - Ni(III) cycle liberating chlorine atoms which react with the C−H bonds of alkanes,
forming alkyl radicals that are trapped by Cl• to form alkyl chlorides. Since alkane
functionalization is not a metal-based process, the regioselectivity of these reactions is
limited to that expected for chlorination with chlorine radicals.
1.5.3.3 Ni(II) catalysts with anionic ligands
Recently, Company and co-workers reported the formation of Ni(IV)-OCl intermediate
from a Ni(II) complex bearing a dianionic macrocyclic ligand (with two amidate, one
pyridine, and one aliphatic amine) upon reaction with NaOCl in the presence of acetic
acid.76
Scheme 27 Possible formulations of compound Ni(IV)-OCl derived from the reaction of 1(Ni-L) with NaOCl in the presence of AcOH. Free energies are given in parentheses in
kcal·mol-1 at -30°C in MeCN.76
The Ni(IV)-OCl intermediate reacted rapidly with substrates including those with strong
aliphatic C−H bonds, and they concluded that in contrast to the previous example
reported by Draksharapu et al. (where nickel generated chloride radicals involved in
chlorination),72 the Ni(IV)-OCl species was directly involved in the oxidation/chlorination
reactions. DFT studies, together with a combination of UV/Vis absorption, EPR, ESI-MS,
Raman, EXAFS spectroscopy enabled the characterization of the intermediate as
23
Chapter 1
formally in the Ni(IV) oxidation state, but in reality it is more accurately formulated as a
Ni(III) complex with one unpaired electron delocalized over the ligand ( Scheme 27).
1.6 Conclusions In summary, NaOCl is a useful oxidant and a high energy species, which can be used in
wide range of functional group transformations. A drawback of hypochlorite is its
reactivity; it reacts rapidly, but with limited specificity. Nevertheless, it has been applied
often with stereo- and chemo-selectivity and its diverse pH chemistry has enabled the
control of its reactivity allowing access to various mechanisms and to tune the reactivity
in the presence of metal complexes as catalysts. A catalyst is typically viewed as a
species that provides a pathway with a lower activation energy than the uncatalyzed
reaction. For example, despite being a high energy molecule, H2O2 does not oxidize
substrates on its own but requires a catalyst. By contrast, NaOCl is highly reactive as the
various oxidation states and species of chlorine act as their own catalyst. Therefore the
challenge is not to accelerate the reaction of NaOCl with substrates but instead to tame
it with a catalyst. In this review it is shown by using various complexes, such as
manganese, iron, and nickel, that NaOCl can be used to generate reactive intermediates,
which have some analogies with natural systems, such as halogenases, haloperoxidase.
Nature produces hypohalites and controls their reactivity with substrates through
hydrogen bonding, proximity effects etc. Alternatively, in case of halogenases,
hypohalites are not formed, but instead an Fe(IV)=O with a chlorido ligand co-ordinates
to the metal center, and a rebound reaction with the chloride ligand involved in the
chlorination of substrates. It is difficult to achieve conditions comparable to those found
in these enzymes, however we can potentially mimic by formation of Fe(IV)=O with a
chlorido ligand present.
Although iron and nickel catalysts have been applied with NaOCl as early as the 1990s,
these system have received little attention compared to manganese complexes,
however over the last decade, high valent iron and nickel intermediates formed with
NaOCl have been characterized. The real challenge, however, is to tame NaOCl, to
generate the active species faster than NaOCl reacts with the substrate directly, which
can be achieved with high concentrations of the catalyst and maintaining low
concentrations of hypochlorite, such that hypochlorite can be reacted to form active
species before having a chance with the substrate and the activated form of the catalyst
can react with substrate. In conclusion, although there are many challenges in the use of
NaOCl in catalyzed reactions, there are also many opportunities provided that we
recognize that activating NaOCl is not the goal but rather taming its reactivity with
suitable metal complexes.
1.7 Outline of the thesis Chapter 1 discusses briefly the production and basic chemistry of the oxidant NaOCl,
focusing on the pH dependence of its reactivity, and enzymes such as halogenases,
24
Introduction
haloperoxidases. The potential for transition metal complexes, based primarily on
manganese, iron and nickel, to tame NaOCl is explored in regard to efforts to use NaOCl
activated species to oxidize the alkanes or alkenes. The aim of chapter 1 is to gain insight
into the high valent intermediates formed with NaOCl and how these complexes can be
applied effectively in selective oxidations.
In chapter 2 the reaction of H2O2 with [(MeN3Py)FeII(CH3CN)2]2+ is studied primarily at
room temperature in acetonitrile. The data reported in the chapter highlight the role of
ligand exchange reactions in the activation of Fe(II), and the importance of the
formation of thermodynamically stable dinuclear Fe(III)−O−Fe(III) species under catalytic
conditions.
In chapter 3 the involvement of high valent iron intermediates in the reaction of
[(MeN3Py)FeII(CH3CN)2]2+ with H2O2 and oxidation of alkenes is discussed. In particular,
the role of solvent (acetonitrile vs acetone) in the chemoselectivity observed, and
especially the role played by the sixth ligand at iron center. It is shown that H2O2 reacts
with [(MeN3Py)FeII(CH3CN)2]2+ in acetone at room temperature and low temperatures (-
15 ºC, -30 ºC, and -80 ºC) results in the formation of Fe(IV)=O as well as Fe(III)-OOH
species, and importantly that the Fe(IV)=O species formed in acetone is distinct from
that formed in acetonitrile. The implications of these differences is discussed in regard
to the differences in chemoselectivity.
Acetic acid is frequently employed in oxidation catalysis with non-heme iron catalysts
and in chapters 2 and 3 its formation in situ and involvement was apparent. In chapter 4,
the goal is to understand the role acetic acid plays in reactivity of
[(MeN3Py)FeII(CH3CN)2]2+ with H2O2 in terms of both the species formed and its influence
on the chemoselectivity of the oxidation of alkenes. Evidence for the formation of an
Fe(IV)=O species in the presence of acetic acid is coupled with an increase in selectivity
towards epoxide products.
In Chapter 5, the aim is to characterize a novel reactive intermediate formed when a
nickel(II) complex of the robust ligand TMTACN reacts with NaOCl. DFT methods
together with time resolved spectroscopy are used to show that reactive species is the
high valent intermediate [(TMTACN)2NiIV2(O)3]2+. Furthermore, initial studies to gain
insight into the reaction mechanism for its formation are reported.
In Chapter 6 the focus shifts to the activation of molecular oxygen and in particular the
application of time resolved resonance Raman spectroscopy to understand the
activation of O2 by Mn(II)dpeo complex. The activation of oxygen by the Mn(II) complex
was followed by a stepwise oxidation of its own ligand at the methylene position to form
a ketone. Importantly, it is shown that the reaction is in fact catalytic and
intermolecular, opening up the possibility for the activation of oxygen beyond ligand
oxidation.
25
Chapter 1
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