# Synthesis and Application of Phenyl Nitrone Derivatives as Acidic and Microbial Corrosion Inhibitors

Authors: Shijun Chen; Kang Zhao; Gang Chen
Journal: Journal of Chemistry
 (2015)

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## Abstract

Nitrone has drawn great attention due to its wide applications as a 1,3-dipole in heterocyclic compounds synthesis and the bioactivities. With the special structure, nitrone can also be used as ligand in inorganic chemistry. Based on the current research, the nitrones are anticipated to be effective inhibitors against acidic and microbial corrosion. The aim of this work is to investigate the inhibitory action of nitrones. In this work, a series of phenyl nitrone derivatives (PN) was synthesized and used as acidic and microbial corrosion inhibitors. The results indicate that several compounds show moderate to high inhibition efficiency (IE) in 3% HCl. Accompanied with HMTA or BOZ, the IEs greatly increase, and the highest efficiency of 98.5% was obtained by using PN4 + BOZ. Investigation of the antibacterial activity against oilfield microorganism shows that the nitrone derivatives can inhibit SRB, IB, and TGB with moderate to high efficiency under 1,000 mg/L, which makes them potential to be used as bifunctional oilfield chemicals.


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## Body

## 1. Introduction

The nitrone is an N-oxide of an amine, which is a 1,3-dipole and is used in 1,3-dipolar cycloadditions and formal[3+3] cycloadditions in the synthesis of many natural products of biological interest with the remarkable region, and stereo selectivity along with efficient incorporation of multiple stereocenters [1]. Many nitrone derivatives are found to possess pharmacological activity and form an essential part of the molecular structure of important drugs [2–4]. Nitrones are generated most often either by the oxidation of hydroxylamines or condensation of aldehyde/ketone and monosubstituted hydroxylamines [5–7]. Recently, some new methods were developed, such as addition reaction of highly reactive allenyl acetates with oximes and a novel Baylis-Hillman reaction [8, 9]. Due to the unique moiety, nitrones have been a fascinating and challenging topic for inorganic chemistry as well. It has been reported that some nitrone compounds can form stable complexes with Cu(II), Ni(II), Co(II), and Cr(III) ions [10], which is useful during the acidic corrosion inhibition for the inhibitors interacting with the metal, so they may be potential corrosion inhibitors. SomeN-diphenyl nitrones have been used as corrosion inhibitors for mild steel in organic acid media, and they were found to be with moderate to high inhibition in 20% formic acid/acetic acid under the concentration of 50 to 150 ppm [11]. It should be noticed that, for most corrosion, the microbiologically influenced corrosion (MIC) cannot be avoided especially in oilfield, so it will be an interesting work to develop inhibitors against acidic corrosion and MIC.These compounds are generally prepared by two main methods: condensation of carbonyl compounds with N-monosubstituted hydroxylamines [12] and oxidation of secondary amines or hydroxylamines [13]. In particular, the oxidative approach provides the most direct and general method for preparing nitrones. Based on the current research, the nitrones are anticipated to be effective inhibitors against acidic and microbial corrosion. The aim of this work is to investigate the inhibitory action of nitrones.


## 2. Experimental

### 2.1. Materials

The corrosion tests were performed on Q235A steel with a composition (in wt%) C: 0.20, P: 0.015, Si: 1.45, S: 0.15, Mn: 0.020, and Fe balance. A small hole of about 3 mm diameter near the upper edge of the coupons was made to help hold them with cotton cords and suspend them into the corrosive medium. Before all measurements, the steel samples were mechanically abraded with increasing grades of emery papers (100, 600, and 1000 grit size) to remove rust particles. The treated coupons were then rinsed by petroleum ether, degreased by ethanol, and dried in air. Finally, the coupons were treated through a procedure that consisted of measuring the length, width, thickness, and diameter and kept in moisture-free desiccators before their immersion in experimental solution. The weights of the specimens were noted before immersion.


### 2.2. Synthesis of Phenyl Nitrone Derivatives

Benzaldehyde derivative (1 mmol), N-methylhydroxylamine hydrochloride (1.1 mmol), and K2CO3 (5 mmol) were mixed in methanol (50 ml). The mixture was refluxed until the disappearance of benzaldehyde derivative, as evidenced by thin-layer chromatography. It was cooled to room temperature and the insoluble residue was filtrated. The solvent was removed in vacuo and the residue was separated by column chromatography (silica gel, petroleum ether/ethyl acetate = 1–3 : 1), giving the target compound. NMR spectra were recorded using a Bruker Drx-400 spectrometer operating at 400 MHz for 1H in CD3OD-CDCl3. Mass spectra were recorded on a Micromass Platform spectrometer using a direct-inlet system operating in the electron impact (EI) mode at 75 eV.


### 2.3. Weight Loss Determination

The corrosion tests were performed on Q235A steel with a composition (in wt%) C: 0.22, P: 0.045, Si: 0.35, S: 0.05, Mn: 1.40, and Fe balance. The electrolyte solution was 1 M HCl, prepared from analytical grade 38% HCl and distilled water. All tests have been performed in water solutions and at 333 ± 0.5°C for 5 h. The gravimetric tests were carried out according to the Standard of Petroleum and Natural Gas Industry of China (Evaluation method for behavior of corrosion inhibitor for produced water of oilfield, SY/T5273-2000) with a few modifications. Each test was done with three specimens at the same time to give reproducible results.


### 2.4. Microbiological Monitoring

Viable counts of sulfate reducing bacteria (SRB), iron bacteria (IB), and total general bacteria (TGB) were determined with the “most probable number” method (China Standard of Petroleum and Natural Gas Industry, the national method of the bactericidal agent’s performance, SY/T 5890-1993). The produced water containing the three kinds of bacteria was gathered from Zichang Oilfield Factory, Yanchang Oilfield.


## 2.1. Materials

The corrosion tests were performed on Q235A steel with a composition (in wt%) C: 0.20, P: 0.015, Si: 1.45, S: 0.15, Mn: 0.020, and Fe balance. A small hole of about 3 mm diameter near the upper edge of the coupons was made to help hold them with cotton cords and suspend them into the corrosive medium. Before all measurements, the steel samples were mechanically abraded with increasing grades of emery papers (100, 600, and 1000 grit size) to remove rust particles. The treated coupons were then rinsed by petroleum ether, degreased by ethanol, and dried in air. Finally, the coupons were treated through a procedure that consisted of measuring the length, width, thickness, and diameter and kept in moisture-free desiccators before their immersion in experimental solution. The weights of the specimens were noted before immersion.


## 2.2. Synthesis of Phenyl Nitrone Derivatives

Benzaldehyde derivative (1 mmol), N-methylhydroxylamine hydrochloride (1.1 mmol), and K2CO3 (5 mmol) were mixed in methanol (50 ml). The mixture was refluxed until the disappearance of benzaldehyde derivative, as evidenced by thin-layer chromatography. It was cooled to room temperature and the insoluble residue was filtrated. The solvent was removed in vacuo and the residue was separated by column chromatography (silica gel, petroleum ether/ethyl acetate = 1–3 : 1), giving the target compound. NMR spectra were recorded using a Bruker Drx-400 spectrometer operating at 400 MHz for 1H in CD3OD-CDCl3. Mass spectra were recorded on a Micromass Platform spectrometer using a direct-inlet system operating in the electron impact (EI) mode at 75 eV.


## 2.3. Weight Loss Determination

The corrosion tests were performed on Q235A steel with a composition (in wt%) C: 0.22, P: 0.045, Si: 0.35, S: 0.05, Mn: 1.40, and Fe balance. The electrolyte solution was 1 M HCl, prepared from analytical grade 38% HCl and distilled water. All tests have been performed in water solutions and at 333 ± 0.5°C for 5 h. The gravimetric tests were carried out according to the Standard of Petroleum and Natural Gas Industry of China (Evaluation method for behavior of corrosion inhibitor for produced water of oilfield, SY/T5273-2000) with a few modifications. Each test was done with three specimens at the same time to give reproducible results.


## 2.4. Microbiological Monitoring

Viable counts of sulfate reducing bacteria (SRB), iron bacteria (IB), and total general bacteria (TGB) were determined with the “most probable number” method (China Standard of Petroleum and Natural Gas Industry, the national method of the bactericidal agent’s performance, SY/T 5890-1993). The produced water containing the three kinds of bacteria was gathered from Zichang Oilfield Factory, Yanchang Oilfield.


## 3. Results and Discussion

### 3.1. Synthesis

Phenyl nitrone derivatives were synthesized as shown in Scheme1. The different substitutes are listed in Table 1. The NMR, MS, yield, and the name of the synthesized compounds were also included in Table 1. From the results, it can be found that the phenyl nitrone derivatives are all in high yield. And most substituted benzaldehydes with electric withdrawing group, such as –NO2 and –Cl, provide higher yield than that with electric donating groups, such as –CH3 and –OH.o-Hydroxy-benzaldehyde gives a relatively higher yield that can be due to the activation of the carbonyl group byo-OH group through the intramolecular hydrogen bond.Table 1
The yield, NMR, and MS of phenyl nitrone derivatives.
R
NMR, MS
Yield (%)
Name
H
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 8.2 (m, 2H), 7.4 (m, 3H), 7.3 (s, 1H), 3.8 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 130.9, 129.9, 129.8, 129.7, 128.8, 128.6, 128.0, 51.0; MS (EI) m/z: 135 (M+)
83.4
PN1
o-OH
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 8.1 (m, 2H), 7.2 (m, 3H), 7.1 (s, 1H), 3.7 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 152.2, 132.0, 131.8, 129.6, 121.8, 118.6, 118.0, 51.2; MS (EI) m/z: 151 (M+)
89.5
PN2
m-OH
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 8.0 (m, 2H), 7.2 (m, 3H), 7.0 (s, 1H), 3.7 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 153.4, 132.1, 131.9, 129.9, 122.0, 117.8, 117.5, 51.0; MS (EI) m/z: 151 (M+)
80.0
PN3
p-OH
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 8.0 (s, 1H), 7.2–7.3 (m, 4H), 7.0 (s, 1H), 3.7 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 142.2, 130.1, 129.9, 129.6, 122.8, 118.2, 118.0, 51.1; MS (EI) m/z: 151 (M+)
83.2
PN4
p-CH3
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 8.1 (m, 1H), 7.4 (m, 3H), 7.3 (s, 1H), 4.2 (s, 3H), 3.8 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 138.5, 129.0, 128.8, 128.6, 127.8, 126.6, 126.5, 51.3, 24.6; MS (EI) m/z: 149 (M+)
79.5
PN5
o-Cl
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 8.3 (m, 2H), 7.3 (m, 3H), 7.1 (s, 1H), 3.8 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 133.9, 129.9, 129.8, 129.6, 128.6, 128.5, 126.0, 51.4; MS (EI) m/z: 169 (M+)
90.5
PN6
p-Cl
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 8.2 (m, 2H), 7.4 (m, 3H), 7.3 (s, 1H), 3.8 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 134.2, 132.1, 131.9, 129.9, 128.8, 128.1, 128.0, 51.3; MS (EI) m/z: 169 (M+)
92.0
PN7
o-NO2
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 9.2 (s, 1H), 8.1 (m, 2H), 7.8 (m, 2H), 7.6 (m, 1H), 3.9 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 150.1, 134.9, 130.2, 129.7, 129.6, 122.4, 121.8, 51.4; MS (EI) m/z: 180 (M+)
96.5
PN8
p-NO2
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 9.1 (s, 1H), 8.1 (m, 2H), 7.7 (m, 2H), 7.6 (m, 1H), 3.9 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 150.9, 139.0, 129.9, 129.4, 129.4, 122.4, 122.2, 51.4; MS (EI) m/z: 180 (M+)
93.2
PN9
2,4-OH
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 8.2 (m, 2H), 7.3 (m, 3H), 7.1 (s, 1H), 3.8 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 160.5, 157.8, 131.8, 129.9, 110.2, 109.6, 108.1, 51.2; MS (EI) m/z: 167 (M+)
92.6
PN10
3,5-OH
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 8.1 (m, 2H), 7.2 (m, 3H), 7.1 (s, 1H), 3.8 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 159.9, 159.2, 132.9, 129.5, 108.4, 108.3, 103.6, 51.3; MS (EI) m/z: 167 (M+)
88.7
PN11Scheme 1
Synthesis of phenyl nitrone derivatives.


### 3.2. Gravimetric Measurements

Corrosion inhibition of Q235A steel by using corrosion inhibitors in 3% HCl solution containing various phenyl nitrone was investigated after immersion at 333 ± 0.5°C for 5 h. Table2 summarizes the inhibition efficiency (IE) from the weight-loss measurements. The results reveal that the structure affects the IE which varies with the substituted groups of phenyl nitrone, and PN4 displays the highest IE of 85.2% compared to PN8 with the lowest IE of 56.3%. Concerning the structures, most of the molecules with electrodonating groups, such as –OH, –CH3, and –OCH3, display relatively high inhibition efficiency, while, with two –OH groups, PN10 and PN11 display relatively low inhibition efficiency, which may be due to the intramolecular and/or intermolecular hydrogen bonding weakening the interaction with the steel.Table 2
Inhibition efficiency of phenyl nitrone for Q235A steel in 3% HCl solution.
Inhibitor
Concentration (mg/L)
IE (%)
PN1
500
75.0
PN2
500
67.8
PN3
500
80.5
PN4
500
85.2
PN5
500
80.5
PN6
500
66.7
PN7
500
65.7
PN8
500
56.3
PN9
500
83.7
PN10
500
65.2
PN11
500
69.6The correlativity between concentration of PN4 and inhibition efficiency was shown in Figure1. The corrosion inhibition efficiency increases sharply as the concentration rising from 100 mg/L to 500 gm/L. As the concentration rising to over 500 mg/L, the efficiency does not rise obviously. The highest IE, 92.3%, is obtained in our study under the concentration of 1000 mg/L.Figure 1
IE of PN4 for Q235A steel dissolution in 3% HCl at different concentrations.


### 3.3. Enhancement by Additives

Hexamethylenetetramine (HMTA) has a symmetric tetrahedral cage-like structure, as shown in Figure2, whose four “corners” are nitrogen atoms and “edges” are methylene groups. The molecule behaves like an amine base, undergoing protonation andN-alkylation. With these features, it has been used as corrosion inhibitor. 1,4-Dihydroxy-2-butyne (BOZ), as shown in Figure 2 containing hydroxyl groups andp-electrons in triple bonds, is also used as a corrosion inhibitor in many conditions, but it was found that the inhibition efficiency is relatively low; moreover much quantity is needed to obtain high inhibition efficiency (about 1–3%), so both are only used as additives in some combined corrosion inhibitors [14]. So HMTA and BOZ were investigated as synergists for the PN4, and the results were shown in Figure 3.Figure 2
The structure of hexamethylenetetramine and 1,4-dihydroxy-2-butyne.Figure 3
The IE of PN4 companied with HMTA or DHBY.From Figure3, it was found that HMTA and BOZ are not efficient inhibitors with the IE of 23.8% and 35.7%, respectively, while they can enhance the IE of PN4 from 85.2% to 95.6% and 98.5%, respectively. The reason should be due to the fruitfulp-electrons of N, O and triple bond, which can form covalent bonds between the molecules and the ion surface, capture H+ to release the acidity, and even link PN4 molecules as “bridges” to enhance the protective film on the ion surface.


### 3.4. Electrochemical Impedance Spectroscopy

The potentiodynamic polarization curves for mild steel in acid solution in the absence and presence of various concentrations of PN4 are shown in Figure4. Extracts at different concentrations lead to different anodic, cathodic Tafel slopes, and the Ecorr values, suggesting that these compounds behave as mixed-type (anodic/cathodic) inhibitors [15]. Increasing inhibition efficiencies with increasing concentration shows that the inhibition occurs because of adsorption on the steel surface [16]. The inhibition efficiencies obtained from potentiodynamic polarization were different from those calculated from weight-loss measurements; the reason is that weight-loss method gives average corrosion rate whereas the electrochemical method gives instantaneous corrosion rates. These variations may also arise because of the different times required to form the adsorbed layer of the inhibitors on metal surface that inhibit corrosion [17].Figure 4
Typical polarization curves for corrosion of Q235A steel in 1 M HCl in the absence and presence of different concentrations of PN4.


### 3.5. Mechanism

It is well known that organic inhibitors establish inhibition by adsorption onto the metal surface, and the adsorption of the organic compounds can be described by two main types of interaction: physical adsorption and chemisorption that are influenced by the nature and charge of the metal, the chemical structure of the inhibitor, and the type of electrolyte. The presence of N, O, and S atoms and conjugated double bonds in the organic structures makes the formation ofp–d bonds resulting from overlap ofp-electrons to the 3d vacant orbital of iron atoms, which enhances the adsorption of the inhibitors on the metal surface [18].The steady conformation of PN4 was expressed in Figure5, which was simulated by a minimized energy of MM2 in Chem 3D, and thep-electrons of the hydroxyl groups were colored in pink. The inhibition efficiency afforded by PN4 may be attributed to the presence of electron-rich nitrone group, phenol group, and phenyl group. The possible reaction centers are unshared electron pair of heteroatoms andp-electrons of phenyl group. The schematic illustration of different modes of adsorption on metal is shown in Figure 6.Figure 5
The steady conformation of PN4.Figure 6
The absorption of PN4 on the steel surface by coordination.


### 3.6. Antibacterial Activity against Oilfield Microorganism

Microbiologically influenced corrosion (MIC) is metal deterioration as a result of the metabolic activity of various microorganisms. This type of corrosion applies to nonmetallic objects as well as metals. For instance, aerobic bacteria such asAcidithiobacillus thiooxidans can cause significant corrosion as they serve as a factor in biogenic sulfide corrosion. As MIC bacteria grow, consumption of the metal in the pipe occurs and sometimes tubercles are formed. Pitting is a likely effect and the walls of the pipe may be penetrated, but the flow characteristics of the pipes are degraded and the loose scale or rust can plug sprinklers and valves. MIC can be prevented through periodic mechanical cleaning, chemical treatment using biocides to prevent bacteria population, and dry storage and total drainage.In oilfield, the MIC is mainly caused by the growth of such microorganism as sulfate reducing bacteria (SRB), iron bacteria (IB), and total general bacteria (TGB) in oil pipelines, which is considered as a major problem for water treatment in the oilfield [19]. MIC can result in different types of attack, such as pitting, crevices, dealloying, and erosion in pipelines [20]. In addition, microbial degradation of crude oil can lead to increased acidity in the oil phase, and the high-acid-contained oil is a problem concerning corrosion of pipelines. Even more serious, the interaction of IB, SRB, and TGB can accelerate the corrosion rate; in other words, the corrosion in the mixture of IB, SRB, and TGB was more serious than in a single microbial system. Based on this case, different treatment systems to inhibit corrosion should be considered, among which using bactericide has received the greatest acceptance. Currently, oxidizer, aldehyde, quaternary ammonium salt, and heterocycle compounds, such as Cl2, ClO2, formaldehyde, pentane-1,5-dial, trichloroisocyanuric acid (TCCA), Schiff base, and some natural products, have been used as bactericides [21–23], but the toxicity and oxidation tests have been conducted on a limited selection.Since the researches have shown nitrone derivatives to be antibacterial active [2–5], the PNs are anticipated to be bactericides for oilfield microorganism. The inhibition of PNs against oilfield microorganism was investigated under the concentrations of 1,000 mg/L, and the results are summarized in Table 3. The results show that the some of the PNs are active against the three microorganisms. For TGB, PN4, PN5, PN6, PN8, and PN10 are very active, for IB almost all PNs are active except PN1 and PN7, and for SRB all PNs display inhibitions, in which PN4, PN9, and PN11 are the top active ones.Table 3
The antifungal activity of PN against oilfield waterborne bacteria.
MGLE
Concentrationmg/L
Microbiotic concentration/mL
TGB
IB
SIB
—
2.5
×
10
4
2.5
×
10
4
2.5
×
10
4
PN1
1,000
2.5
×
10
3
7.0
×
10
2
2.5
×
10
2
PN2
1,000
2.5
×
10
4
2.5
×
10
1
2.5
×
10
2
PN3
1,000
7.0
×
10
3
1.1
×
10
1
2.5
×
10
2
PN4
1,000
0.9
×
10
1
2.5
×
10
0
2.5
×
10
0
PN5
1,000
0.9
×
10
1
1.1
×
10
0
2.5
×
10
1
PN6
1,000
0.9
×
10
2
7.0
×
10
0
1.1
×
10
2
PN7
1,000
2.5
×
10
4
2.5
×
10
3
2.5
×
10
1
PN8
1,000
0.9
×
10
1
2.5
×
10
0
2.5
×
10
1
PN9
1,000
2.5
×
10
2
0.9
×
10
0
0
×
10
0
PN10
1,000
2.5
×
10
1
7.0
×
10
1
2.5
×
10
2
PN11
1,000
0.9
×
10
4
2.5
×
10
0
2.5
×
10
0


## 3.1. Synthesis

Phenyl nitrone derivatives were synthesized as shown in Scheme1. The different substitutes are listed in Table 1. The NMR, MS, yield, and the name of the synthesized compounds were also included in Table 1. From the results, it can be found that the phenyl nitrone derivatives are all in high yield. And most substituted benzaldehydes with electric withdrawing group, such as –NO2 and –Cl, provide higher yield than that with electric donating groups, such as –CH3 and –OH.o-Hydroxy-benzaldehyde gives a relatively higher yield that can be due to the activation of the carbonyl group byo-OH group through the intramolecular hydrogen bond.Table 1
The yield, NMR, and MS of phenyl nitrone derivatives.
R
NMR, MS
Yield (%)
Name
H
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 8.2 (m, 2H), 7.4 (m, 3H), 7.3 (s, 1H), 3.8 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 130.9, 129.9, 129.8, 129.7, 128.8, 128.6, 128.0, 51.0; MS (EI) m/z: 135 (M+)
83.4
PN1
o-OH
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 8.1 (m, 2H), 7.2 (m, 3H), 7.1 (s, 1H), 3.7 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 152.2, 132.0, 131.8, 129.6, 121.8, 118.6, 118.0, 51.2; MS (EI) m/z: 151 (M+)
89.5
PN2
m-OH
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 8.0 (m, 2H), 7.2 (m, 3H), 7.0 (s, 1H), 3.7 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 153.4, 132.1, 131.9, 129.9, 122.0, 117.8, 117.5, 51.0; MS (EI) m/z: 151 (M+)
80.0
PN3
p-OH
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 8.0 (s, 1H), 7.2–7.3 (m, 4H), 7.0 (s, 1H), 3.7 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 142.2, 130.1, 129.9, 129.6, 122.8, 118.2, 118.0, 51.1; MS (EI) m/z: 151 (M+)
83.2
PN4
p-CH3
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 8.1 (m, 1H), 7.4 (m, 3H), 7.3 (s, 1H), 4.2 (s, 3H), 3.8 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 138.5, 129.0, 128.8, 128.6, 127.8, 126.6, 126.5, 51.3, 24.6; MS (EI) m/z: 149 (M+)
79.5
PN5
o-Cl
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 8.3 (m, 2H), 7.3 (m, 3H), 7.1 (s, 1H), 3.8 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 133.9, 129.9, 129.8, 129.6, 128.6, 128.5, 126.0, 51.4; MS (EI) m/z: 169 (M+)
90.5
PN6
p-Cl
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 8.2 (m, 2H), 7.4 (m, 3H), 7.3 (s, 1H), 3.8 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 134.2, 132.1, 131.9, 129.9, 128.8, 128.1, 128.0, 51.3; MS (EI) m/z: 169 (M+)
92.0
PN7
o-NO2
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 9.2 (s, 1H), 8.1 (m, 2H), 7.8 (m, 2H), 7.6 (m, 1H), 3.9 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 150.1, 134.9, 130.2, 129.7, 129.6, 122.4, 121.8, 51.4; MS (EI) m/z: 180 (M+)
96.5
PN8
p-NO2
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 9.1 (s, 1H), 8.1 (m, 2H), 7.7 (m, 2H), 7.6 (m, 1H), 3.9 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 150.9, 139.0, 129.9, 129.4, 129.4, 122.4, 122.2, 51.4; MS (EI) m/z: 180 (M+)
93.2
PN9
2,4-OH
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 8.2 (m, 2H), 7.3 (m, 3H), 7.1 (s, 1H), 3.8 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 160.5, 157.8, 131.8, 129.9, 110.2, 109.6, 108.1, 51.2; MS (EI) m/z: 167 (M+)
92.6
PN10
3,5-OH
1H NMR (CD3OD-CDCl3, 400 MHz), δ: 8.1 (m, 2H), 7.2 (m, 3H), 7.1 (s, 1H), 3.8 (s, 3H); 13C NMR (CD3OD-CDCl3, 100 MHz), δ: 159.9, 159.2, 132.9, 129.5, 108.4, 108.3, 103.6, 51.3; MS (EI) m/z: 167 (M+)
88.7
PN11Scheme 1
Synthesis of phenyl nitrone derivatives.


## 3.2. Gravimetric Measurements

Corrosion inhibition of Q235A steel by using corrosion inhibitors in 3% HCl solution containing various phenyl nitrone was investigated after immersion at 333 ± 0.5°C for 5 h. Table2 summarizes the inhibition efficiency (IE) from the weight-loss measurements. The results reveal that the structure affects the IE which varies with the substituted groups of phenyl nitrone, and PN4 displays the highest IE of 85.2% compared to PN8 with the lowest IE of 56.3%. Concerning the structures, most of the molecules with electrodonating groups, such as –OH, –CH3, and –OCH3, display relatively high inhibition efficiency, while, with two –OH groups, PN10 and PN11 display relatively low inhibition efficiency, which may be due to the intramolecular and/or intermolecular hydrogen bonding weakening the interaction with the steel.Table 2
Inhibition efficiency of phenyl nitrone for Q235A steel in 3% HCl solution.
Inhibitor
Concentration (mg/L)
IE (%)
PN1
500
75.0
PN2
500
67.8
PN3
500
80.5
PN4
500
85.2
PN5
500
80.5
PN6
500
66.7
PN7
500
65.7
PN8
500
56.3
PN9
500
83.7
PN10
500
65.2
PN11
500
69.6The correlativity between concentration of PN4 and inhibition efficiency was shown in Figure1. The corrosion inhibition efficiency increases sharply as the concentration rising from 100 mg/L to 500 gm/L. As the concentration rising to over 500 mg/L, the efficiency does not rise obviously. The highest IE, 92.3%, is obtained in our study under the concentration of 1000 mg/L.Figure 1
IE of PN4 for Q235A steel dissolution in 3% HCl at different concentrations.


## 3.3. Enhancement by Additives

Hexamethylenetetramine (HMTA) has a symmetric tetrahedral cage-like structure, as shown in Figure2, whose four “corners” are nitrogen atoms and “edges” are methylene groups. The molecule behaves like an amine base, undergoing protonation andN-alkylation. With these features, it has been used as corrosion inhibitor. 1,4-Dihydroxy-2-butyne (BOZ), as shown in Figure 2 containing hydroxyl groups andp-electrons in triple bonds, is also used as a corrosion inhibitor in many conditions, but it was found that the inhibition efficiency is relatively low; moreover much quantity is needed to obtain high inhibition efficiency (about 1–3%), so both are only used as additives in some combined corrosion inhibitors [14]. So HMTA and BOZ were investigated as synergists for the PN4, and the results were shown in Figure 3.Figure 2
The structure of hexamethylenetetramine and 1,4-dihydroxy-2-butyne.Figure 3
The IE of PN4 companied with HMTA or DHBY.From Figure3, it was found that HMTA and BOZ are not efficient inhibitors with the IE of 23.8% and 35.7%, respectively, while they can enhance the IE of PN4 from 85.2% to 95.6% and 98.5%, respectively. The reason should be due to the fruitfulp-electrons of N, O and triple bond, which can form covalent bonds between the molecules and the ion surface, capture H+ to release the acidity, and even link PN4 molecules as “bridges” to enhance the protective film on the ion surface.


## 3.4. Electrochemical Impedance Spectroscopy

The potentiodynamic polarization curves for mild steel in acid solution in the absence and presence of various concentrations of PN4 are shown in Figure4. Extracts at different concentrations lead to different anodic, cathodic Tafel slopes, and the Ecorr values, suggesting that these compounds behave as mixed-type (anodic/cathodic) inhibitors [15]. Increasing inhibition efficiencies with increasing concentration shows that the inhibition occurs because of adsorption on the steel surface [16]. The inhibition efficiencies obtained from potentiodynamic polarization were different from those calculated from weight-loss measurements; the reason is that weight-loss method gives average corrosion rate whereas the electrochemical method gives instantaneous corrosion rates. These variations may also arise because of the different times required to form the adsorbed layer of the inhibitors on metal surface that inhibit corrosion [17].Figure 4
Typical polarization curves for corrosion of Q235A steel in 1 M HCl in the absence and presence of different concentrations of PN4.


## 3.5. Mechanism

It is well known that organic inhibitors establish inhibition by adsorption onto the metal surface, and the adsorption of the organic compounds can be described by two main types of interaction: physical adsorption and chemisorption that are influenced by the nature and charge of the metal, the chemical structure of the inhibitor, and the type of electrolyte. The presence of N, O, and S atoms and conjugated double bonds in the organic structures makes the formation ofp–d bonds resulting from overlap ofp-electrons to the 3d vacant orbital of iron atoms, which enhances the adsorption of the inhibitors on the metal surface [18].The steady conformation of PN4 was expressed in Figure5, which was simulated by a minimized energy of MM2 in Chem 3D, and thep-electrons of the hydroxyl groups were colored in pink. The inhibition efficiency afforded by PN4 may be attributed to the presence of electron-rich nitrone group, phenol group, and phenyl group. The possible reaction centers are unshared electron pair of heteroatoms andp-electrons of phenyl group. The schematic illustration of different modes of adsorption on metal is shown in Figure 6.Figure 5
The steady conformation of PN4.Figure 6
The absorption of PN4 on the steel surface by coordination.


## 3.6. Antibacterial Activity against Oilfield Microorganism

Microbiologically influenced corrosion (MIC) is metal deterioration as a result of the metabolic activity of various microorganisms. This type of corrosion applies to nonmetallic objects as well as metals. For instance, aerobic bacteria such asAcidithiobacillus thiooxidans can cause significant corrosion as they serve as a factor in biogenic sulfide corrosion. As MIC bacteria grow, consumption of the metal in the pipe occurs and sometimes tubercles are formed. Pitting is a likely effect and the walls of the pipe may be penetrated, but the flow characteristics of the pipes are degraded and the loose scale or rust can plug sprinklers and valves. MIC can be prevented through periodic mechanical cleaning, chemical treatment using biocides to prevent bacteria population, and dry storage and total drainage.In oilfield, the MIC is mainly caused by the growth of such microorganism as sulfate reducing bacteria (SRB), iron bacteria (IB), and total general bacteria (TGB) in oil pipelines, which is considered as a major problem for water treatment in the oilfield [19]. MIC can result in different types of attack, such as pitting, crevices, dealloying, and erosion in pipelines [20]. In addition, microbial degradation of crude oil can lead to increased acidity in the oil phase, and the high-acid-contained oil is a problem concerning corrosion of pipelines. Even more serious, the interaction of IB, SRB, and TGB can accelerate the corrosion rate; in other words, the corrosion in the mixture of IB, SRB, and TGB was more serious than in a single microbial system. Based on this case, different treatment systems to inhibit corrosion should be considered, among which using bactericide has received the greatest acceptance. Currently, oxidizer, aldehyde, quaternary ammonium salt, and heterocycle compounds, such as Cl2, ClO2, formaldehyde, pentane-1,5-dial, trichloroisocyanuric acid (TCCA), Schiff base, and some natural products, have been used as bactericides [21–23], but the toxicity and oxidation tests have been conducted on a limited selection.Since the researches have shown nitrone derivatives to be antibacterial active [2–5], the PNs are anticipated to be bactericides for oilfield microorganism. The inhibition of PNs against oilfield microorganism was investigated under the concentrations of 1,000 mg/L, and the results are summarized in Table 3. The results show that the some of the PNs are active against the three microorganisms. For TGB, PN4, PN5, PN6, PN8, and PN10 are very active, for IB almost all PNs are active except PN1 and PN7, and for SRB all PNs display inhibitions, in which PN4, PN9, and PN11 are the top active ones.Table 3
The antifungal activity of PN against oilfield waterborne bacteria.
MGLE
Concentrationmg/L
Microbiotic concentration/mL
TGB
IB
SIB
—
2.5
×
10
4
2.5
×
10
4
2.5
×
10
4
PN1
1,000
2.5
×
10
3
7.0
×
10
2
2.5
×
10
2
PN2
1,000
2.5
×
10
4
2.5
×
10
1
2.5
×
10
2
PN3
1,000
7.0
×
10
3
1.1
×
10
1
2.5
×
10
2
PN4
1,000
0.9
×
10
1
2.5
×
10
0
2.5
×
10
0
PN5
1,000
0.9
×
10
1
1.1
×
10
0
2.5
×
10
1
PN6
1,000
0.9
×
10
2
7.0
×
10
0
1.1
×
10
2
PN7
1,000
2.5
×
10
4
2.5
×
10
3
2.5
×
10
1
PN8
1,000
0.9
×
10
1
2.5
×
10
0
2.5
×
10
1
PN9
1,000
2.5
×
10
2
0.9
×
10
0
0
×
10
0
PN10
1,000
2.5
×
10
1
7.0
×
10
1
2.5
×
10
2
PN11
1,000
0.9
×
10
4
2.5
×
10
0
2.5
×
10
0


## 4. Conclusion

In this work, a series of phenyl nitrone derivatives (PN) was synthesized and characterized. Then the corrosion inhibition efficiency and the mechanism of these nitrone derivatives were investigated. The results indicate that several compounds show high IE of over 80% in 3% HCl. Accompanied with HMTA or BOZ, the IEs greatly increase, and the highest efficiency of 98.5% was obtained by using PN4 + BOZ. Investigation of the antibacterial activity against oilfield microorganism shows that the nitrone derivatives can inhibit SRB, IB, and TGB with moderate to high efficiency under 1,000 mg/L, which makes them potential to be used as bifunctional oilfield chemicals.



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*Source: 201259-2015-06-10.xml*