# A Novel Molecularly Imprinted Polymer for the Selective Removal of Chlorophyll from Heavily Pigmented Green Plant Extracts prior to Instrumental Analysis

Authors: Bareki Shima Batlokwa; Janes Mokgadi; Ronald Majors; Charlotta Turner; Nelson Torto
Journal: Journal of Chemistry
 (2013)

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## Abstract

A novel molecularly imprinted polymer (MIP) powder designed for the selective removal of interfering chlorophyll pigment from heavily pigmented green plant extracts during pesticide residue analysis or analysis for bioactives in natural product research is reported. The polymer powder imprinted with chlorophylla was synthesized by copolymerizing the functional and cross-linking monomers, methacrylic acid (MAA) and ethylene glycol dimethacrylate (EGDMA),  respectively. During batch rebinding experiments, the MIP effectively removed chlorophyll from neat chlorophyll standards, green medicinal plants, and spinach extracts with determined absorbance as high as 2.501 absorbance units (Au) to as low as 0.084 Au after the optimum quantity of the MIP (170 mg mL−1) was added as the adsorbent prior to instrumental analysis. The determined 0.084 Au absorbance was far below the absorbance of 2% chlorophyll (0.401 Au) regarded as the cut-off point for interfering chlorophyll. Thus the newly developed polymer presents itself as a suitable adsorbent for the selective removal of chlorophyll from heavily pigmented, chlorophyll
containing extracts.


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## Body

## 1. Introduction

Chlorophyll the green pigment found in all photosynthetic plants as well as in some bacteria, often interferes with the quantitative analysis of bioactives in natural product research or in pesticide residue analysis [1]. For example, in the Quick Easy Cheap Effective Rugged Safe (QuEChERS) technique, extracts of green vegetables like spinach which are highly pigmented with chlorophyll, challenge the analytical portion of the method during pesticide residue analysis [2]. Such a type of matrix introduces severe interferences in the analytical separation step. Moreover, very “dirty” samples exhibit a noxious property of strongly influencing the background ion current in mass spectrometry (MS) detectors, thus reducing their sensitivities [3]. Of consequence, quantitative analysis can be achieved only after extensive clean-up step(s) [4]. Currently graphitized carbon black (GCB) is employed in the dispersive SPE kits of QuEChERS in order to remove the high levels of the green pigment from the vegetable matrix. However GCB does not only remove chlorophyll, but it also retains pesticides with planar structures resulting in poor recovery and precision [5]. Moreover it is very expensive.In order to address the challenges of GCB on planar pesticides or bioactives recoveries, a sample preparation step employing cheap, selective materials should be developed so that only the interfering chlorophyll is removed prior to pesticide residue or bioactive analysis. An example of such materials is the molecular imprinted polymers (MIPs). They are synthetic polymers with selective recognition sites that have been created during imprinting with a template which is usually the target molecule. MIPs have seen increased use in contaminant or trace analysis as suitable materials for applications where analyte selectivity is essential [6]. They have been shown to be suitable as sorbent materials for solid phase extraction [7–12], hence providing a selective clean-up and preconcentration step for samples normally associated with complex matrices.This paper presents preliminary results for the preparation and evaluation of the effectiveness of a novel, simply and cheaply prepared MIP for the specific removal of chlorophyll from green plants extracts relative to the performance offered by the expensive, nonspecific GCB which has been in use.


## 2. Experimental

### 2.1. Chemicals

Chlorophylla standard, hexachlorobenzene (HCB), dichlorodiphenyldichloroethylene (DDE), dichlorodiphenyldichloroethane (DDD), graphitized carbon black (GCB), methacrylic acid (MAA), ethylene glycol dimethacrylate (EGDMA), dichloromethane (DCM), HPLC grade methanol and azobisisobutyronitrile (AIBN), and sodium acetate/acetic acid buffer were supplied by Sigma-Aldrich (Saint Louis, MO, USA). Fresh spinach was bought from a local shop (Grahamstown, South Africa). Reagents used were of analytical grade or better. All water used was purified using a Direct Q 3UV Millipore system. Tswii (Nymphaea lotus) and Makgonatsotlhe (Acalypha villicaulis) leaves are traditional medicines collected from the Okavango Delta area in Botswana (Okavango Delta, Botswana).


### 2.2. Instrumentation and Apparatus

A lambda 25 Perkin-Elmer spectrophotometer, by Perkin-Elmer, (Santa Clara, CA, USA) was used to detect the concentration of chlorophyll (at 680 nm, using a 1 cm cell) in every washing during template removal and the supernatant after addition of the MIP during batch rebinding experiments. Agilent GC-6820 (Santa Clara, CA, USA) equipped withNi63 electron capture detector and DB-5 MS fused-silica capillary column (30 m length, 0.25 mm internal diameter, and 0.25 μm film thickness) were employed in the separation and determination of the concentrations of planar pesticides that were coextracted with the interfering chlorophyll. GC analytical conditions used were as follows: oven temperature programming: 50°C (hold time: 1 min), raised to 145°C at 30°C min−1 (3 min), to 260°C at 20°C min−1 (3 min), and finally to 300°C at 10°C min−1 (3 min). The injector and detector temperatures were held at 280°C and 300°C, respectively. Helium flowing at 2 mL min−1 was used as the carrier gas while nitrogen was the make-up gas at 1.3 mL min−1. 1 μL sample was injected in the splitless mode. An MSE Mistral 1000 by Sanyo Gallenkamp, (Loughborough, England) was employed for centrifugation. Standard Test sieves by Retsch GmbH & Co. (Haan, Germany) were used to obtain the average size of the polymer particles by screen analysis.


### 2.3. Preparation of the Chlorophyll Molecular Imprinted Polymer (MIP)

For the preparation of the molecularly imprinted polymers (MIPs), chlorophylla, MAA, EGDMA, and AIBN in the mole ratio 1 : 5 : 25 : 0.4 were dissolved in 35 mL of DCM, respectively. The mixture was purged with nitrogen for 10 min and refluxed on an oil bath at 75°C for 9 h. The resultant rigid polymer was ground to a powder of particles sizes of less than 45 μm in diameter after which the template was thoroughly removed following the pressurized hot water extraction approach proposed by Batlokwa et al. [13] with slight modifications. Thereafter, the particles were left to dry in open air overnight. A reference polymer referred to as a nonimprinted polymer (NIP), without the imprinting template chlorophyll a, was prepared with a similar procedure to provide for the control in the rebinding experiments.


### 2.4. Optimization of MIP Quantity Needed for Maximum Removal of Chlorophyll

Increasing quantities of MIP were added to 5 mL aliquots of 10% (w/v) chlorophyll. They were then equilibrated for 24 h at pH 7 in sodium acetate/acetic acid buffer and centrifuged for 5 min. The absorbance of chlorophyll in the supernatant was determined with a UV spectrophotometer until there were constant readings with further additions of the MIP. Leaching experiments from the MIP particles were performed following a procedure by Batlokwa et al. [13] to confirm the absorbances determined in the supernatants. The experiments were carried out in triplicates, and the average % bound to the MIP was calculated. Statistical methods were used to determine the mean values and the percentage standard deviations (% RSD). From the values, a plot of absorbance against quantity of MIP added as the adsorbent was constructed.


### 2.5. Optimization of Time Needed for Maximum Removal of Chlorophyll

Following the procedure for optimization of quantity, absorbance of chlorophyll in the supernatant was monitored at 5 min intervals until a constant value of absorbance was reached. This marked the optimum time needed for the polymer to bind maximally.


#### 2.5.1. Selectivity Experiments

Employing the optimized conditions, competitive and nonselectivity experiments were performed. Both the imprinted and nonimprinted polymers were used to obtain two sets of experimental data. 850 mg polymer material or GCB was added to 5 mL aliquots containing a 10% (w/v) chlorophyll standard, 1μg mL−1 of each of the pesticides, HCB, DDD, and DDE. The same procedure was repeated for a mixture of chlorophyll and all the pesticides in order to cater for their coexistence. Column GC-ECD was employed in the seperation and determination of the concentrations of the pesticides.


### 2.6. Effectiveness of the MIP, NIP, and GCB in Removing Chlorophyll from Spinach and Traditional Medicine Plant Leaves Extracts

To obtain chlorophyll from spinach and traditional medicine plant leaves, 10 g of each was blended with 80 mL methanol for 5 min, and the green supernatants were used as test samples. The initial absorbance for each of the extracts was determined after which the optimized quantity of MIP, 850 mg, was added to 5 mL extracts, equilibrated for 5 min, and then centrifuged for another 5 min.  The absorbance of the supernatants was then determined and compared to that of a 2% chlorophyll standard, below which chlorophyll is claimed not to interfere with analysis [1].


## 2.1. Chemicals

Chlorophylla standard, hexachlorobenzene (HCB), dichlorodiphenyldichloroethylene (DDE), dichlorodiphenyldichloroethane (DDD), graphitized carbon black (GCB), methacrylic acid (MAA), ethylene glycol dimethacrylate (EGDMA), dichloromethane (DCM), HPLC grade methanol and azobisisobutyronitrile (AIBN), and sodium acetate/acetic acid buffer were supplied by Sigma-Aldrich (Saint Louis, MO, USA). Fresh spinach was bought from a local shop (Grahamstown, South Africa). Reagents used were of analytical grade or better. All water used was purified using a Direct Q 3UV Millipore system. Tswii (Nymphaea lotus) and Makgonatsotlhe (Acalypha villicaulis) leaves are traditional medicines collected from the Okavango Delta area in Botswana (Okavango Delta, Botswana).


## 2.2. Instrumentation and Apparatus

A lambda 25 Perkin-Elmer spectrophotometer, by Perkin-Elmer, (Santa Clara, CA, USA) was used to detect the concentration of chlorophyll (at 680 nm, using a 1 cm cell) in every washing during template removal and the supernatant after addition of the MIP during batch rebinding experiments. Agilent GC-6820 (Santa Clara, CA, USA) equipped withNi63 electron capture detector and DB-5 MS fused-silica capillary column (30 m length, 0.25 mm internal diameter, and 0.25 μm film thickness) were employed in the separation and determination of the concentrations of planar pesticides that were coextracted with the interfering chlorophyll. GC analytical conditions used were as follows: oven temperature programming: 50°C (hold time: 1 min), raised to 145°C at 30°C min−1 (3 min), to 260°C at 20°C min−1 (3 min), and finally to 300°C at 10°C min−1 (3 min). The injector and detector temperatures were held at 280°C and 300°C, respectively. Helium flowing at 2 mL min−1 was used as the carrier gas while nitrogen was the make-up gas at 1.3 mL min−1. 1 μL sample was injected in the splitless mode. An MSE Mistral 1000 by Sanyo Gallenkamp, (Loughborough, England) was employed for centrifugation. Standard Test sieves by Retsch GmbH & Co. (Haan, Germany) were used to obtain the average size of the polymer particles by screen analysis.


## 2.3. Preparation of the Chlorophyll Molecular Imprinted Polymer (MIP)

For the preparation of the molecularly imprinted polymers (MIPs), chlorophylla, MAA, EGDMA, and AIBN in the mole ratio 1 : 5 : 25 : 0.4 were dissolved in 35 mL of DCM, respectively. The mixture was purged with nitrogen for 10 min and refluxed on an oil bath at 75°C for 9 h. The resultant rigid polymer was ground to a powder of particles sizes of less than 45 μm in diameter after which the template was thoroughly removed following the pressurized hot water extraction approach proposed by Batlokwa et al. [13] with slight modifications. Thereafter, the particles were left to dry in open air overnight. A reference polymer referred to as a nonimprinted polymer (NIP), without the imprinting template chlorophyll a, was prepared with a similar procedure to provide for the control in the rebinding experiments.


## 2.4. Optimization of MIP Quantity Needed for Maximum Removal of Chlorophyll

Increasing quantities of MIP were added to 5 mL aliquots of 10% (w/v) chlorophyll. They were then equilibrated for 24 h at pH 7 in sodium acetate/acetic acid buffer and centrifuged for 5 min. The absorbance of chlorophyll in the supernatant was determined with a UV spectrophotometer until there were constant readings with further additions of the MIP. Leaching experiments from the MIP particles were performed following a procedure by Batlokwa et al. [13] to confirm the absorbances determined in the supernatants. The experiments were carried out in triplicates, and the average % bound to the MIP was calculated. Statistical methods were used to determine the mean values and the percentage standard deviations (% RSD). From the values, a plot of absorbance against quantity of MIP added as the adsorbent was constructed.


## 2.5. Optimization of Time Needed for Maximum Removal of Chlorophyll

Following the procedure for optimization of quantity, absorbance of chlorophyll in the supernatant was monitored at 5 min intervals until a constant value of absorbance was reached. This marked the optimum time needed for the polymer to bind maximally.


### 2.5.1. Selectivity Experiments

Employing the optimized conditions, competitive and nonselectivity experiments were performed. Both the imprinted and nonimprinted polymers were used to obtain two sets of experimental data. 850 mg polymer material or GCB was added to 5 mL aliquots containing a 10% (w/v) chlorophyll standard, 1μg mL−1 of each of the pesticides, HCB, DDD, and DDE. The same procedure was repeated for a mixture of chlorophyll and all the pesticides in order to cater for their coexistence. Column GC-ECD was employed in the seperation and determination of the concentrations of the pesticides.


## 2.5.1. Selectivity Experiments

Employing the optimized conditions, competitive and nonselectivity experiments were performed. Both the imprinted and nonimprinted polymers were used to obtain two sets of experimental data. 850 mg polymer material or GCB was added to 5 mL aliquots containing a 10% (w/v) chlorophyll standard, 1μg mL−1 of each of the pesticides, HCB, DDD, and DDE. The same procedure was repeated for a mixture of chlorophyll and all the pesticides in order to cater for their coexistence. Column GC-ECD was employed in the seperation and determination of the concentrations of the pesticides.


## 2.6. Effectiveness of the MIP, NIP, and GCB in Removing Chlorophyll from Spinach and Traditional Medicine Plant Leaves Extracts

To obtain chlorophyll from spinach and traditional medicine plant leaves, 10 g of each was blended with 80 mL methanol for 5 min, and the green supernatants were used as test samples. The initial absorbance for each of the extracts was determined after which the optimized quantity of MIP, 850 mg, was added to 5 mL extracts, equilibrated for 5 min, and then centrifuged for another 5 min.  The absorbance of the supernatants was then determined and compared to that of a 2% chlorophyll standard, below which chlorophyll is claimed not to interfere with analysis [1].


## 3. Results and Discussion

### 3.1. Optimized Quantity of MIP Needed for Maximum Removal of Chlorophyll

The absorbance (concentration) of chlorophyll decreased with an increase in the quantity of MIP added until an optimal value of 850 mg in the 5 mL chlorophyll standard solutions (see Figure1) was reached. According to Mastovska and Lehotay and our own findings, 300 mg of GCB (550 mg less than the quantity of the MIP we prepared) was needed to remove an equivalent concentration of chlorophyll [14]. The prepared polymer removed chlorophyll up to a very low absorbance (0.081 Au) when compared to the absorbance of 0.399 Au that is said to interfere with the analysis [1], which is the absorbance of a 2% (w/v) chlorophyll standard.Figure 1
Optimization of the quantity of MIP needed to remove maximum chlorophyll in 24 h at pH 7.n=3.


### 3.2. Optimization of Time Needed to Remove Chlorophyll Maximally

Figure2 showed the time dependence of the MIP in removing chlorophyll. Optimum chlorophyll removal as indicated by the leveling off of the plot was achieved at 6 min which is comparable to the fast kinetics exhibited by GCB (4.5 min) in removing chlorophyll [14].Figure 2
Optimization of the time needed for maximum removal of chlorophyll, at optimal MIP quantity of 850 mg and pH 7.n=3.


#### 3.2.1. Selectivity Experiments

To investigate selectivity, both the planar pesticides and the interfering species (chlorophyll) were exposed to the MIP as well as to GCB as single entities and in a mixture form at optimum conditions. In all cases the MIP did not bind any of the planar pesticides while the percentage of chlorophyll bound was over 99.75% (see Table1). GCB on the other hand did not show any specific selectivity towards any of the analytes as it bound over 88% of each of the planar pesticides as well as the chlorophyll from their prepared standard solutions. It should be noted that the same experiments were performed with the NIP which also exhibited no specific selectivity as all of the analytes were bound just like with GCB. However the percentages bound by the NIP were very low, less than 3.7% in all cases, and as such were considered negligible.Table 1
A Comparison of selectivity of various adsorbents in specifically binding chlorophyll and/or pesticides at optimized conditions.
Analyte/interferent
% bound to MIP
% bound to GCB
% bound to NIP
n
=
3
n
=
3
n
=
3
Chlorophyll (spinach extract)
99.86 (0.72)
99.92 (1.01)
2.96 (0.19)
Chlorophyll (Nymphaealotus extract)
99.90 (0.64)
99.95 (0.83)
3.66 (0.09)
Chlorophyll (Acalyphavillicaulis extract)
99.86 (0.97)
99.88 (1.06)
2.42 (0.04)
HCB
nq
90.41 (1.67)
3.61 (0.28)
DDE
nq
89.97 (0.93)
3.44 (0.01)
DDD
nq
91.28 (1.38)
3.29 (0.14)
Mixture
Chlorophyll
99.79 (1.03)
88.94 (0.73)
3.22 (0.36)
HCB
nq
94.52 (1.84)
3.49 (0.92)
DDE
nq
90.26 (1.51)
2.79 (0.02)
DDD
nq
93.08 (1.96)
3.58 (0.16)
Values in parenthesis are % RSD, and nq is for not quantifiable.GCB was able to bind higher quantities of the analytes than the NIP because it has a layered, planar structure which easily flushed with those of the planar pesticides. The NIPs on the other hand have a three-dimensional (3D) highly cross-linked structure with no recognition sites that could allow them to highly bind the pesticides or the chlorophyll. In addition to the imprints within the MIP structure, the high specificity of the prepared MIP to the chlorophyll was thought to be due to the bulkiness of the 3D structure of the chlorophyll locking with the 3D, highly cross-linked MIP structure.


### 3.3. Effectiveness of Chlorophyll Removal from Spinach Leaves Extract

The initial chlorophyll absorbance of the methanolic, spinach extract was reduced from 0.683 to as low as 0.092 Au after the addition of the MIP. For the traditional medicine extracts there was removal from a chlorophyll absorbance of 0.795 to 0.0897 Au inNymph lotusand 0.649 to 0.0899 Au in Acalypha villicaulis. In all cases, the MIP had significantly removed the interfering chlorophyll to absorbance values far below what is regarded as the interfering chlorophyll which is the absorbance of a 2% (w/v) chlorophyll standard determined to be 0.401 Au (the literature value is 0.399 Au) [1]. This was also marked by the loss of the green characteristic color of the plant extracts to almost colorless solutions after exposure to the MIP powder.


## 3.1. Optimized Quantity of MIP Needed for Maximum Removal of Chlorophyll

The absorbance (concentration) of chlorophyll decreased with an increase in the quantity of MIP added until an optimal value of 850 mg in the 5 mL chlorophyll standard solutions (see Figure1) was reached. According to Mastovska and Lehotay and our own findings, 300 mg of GCB (550 mg less than the quantity of the MIP we prepared) was needed to remove an equivalent concentration of chlorophyll [14]. The prepared polymer removed chlorophyll up to a very low absorbance (0.081 Au) when compared to the absorbance of 0.399 Au that is said to interfere with the analysis [1], which is the absorbance of a 2% (w/v) chlorophyll standard.Figure 1
Optimization of the quantity of MIP needed to remove maximum chlorophyll in 24 h at pH 7.n=3.


## 3.2. Optimization of Time Needed to Remove Chlorophyll Maximally

Figure2 showed the time dependence of the MIP in removing chlorophyll. Optimum chlorophyll removal as indicated by the leveling off of the plot was achieved at 6 min which is comparable to the fast kinetics exhibited by GCB (4.5 min) in removing chlorophyll [14].Figure 2
Optimization of the time needed for maximum removal of chlorophyll, at optimal MIP quantity of 850 mg and pH 7.n=3.


### 3.2.1. Selectivity Experiments

To investigate selectivity, both the planar pesticides and the interfering species (chlorophyll) were exposed to the MIP as well as to GCB as single entities and in a mixture form at optimum conditions. In all cases the MIP did not bind any of the planar pesticides while the percentage of chlorophyll bound was over 99.75% (see Table1). GCB on the other hand did not show any specific selectivity towards any of the analytes as it bound over 88% of each of the planar pesticides as well as the chlorophyll from their prepared standard solutions. It should be noted that the same experiments were performed with the NIP which also exhibited no specific selectivity as all of the analytes were bound just like with GCB. However the percentages bound by the NIP were very low, less than 3.7% in all cases, and as such were considered negligible.Table 1
A Comparison of selectivity of various adsorbents in specifically binding chlorophyll and/or pesticides at optimized conditions.
Analyte/interferent
% bound to MIP
% bound to GCB
% bound to NIP
n
=
3
n
=
3
n
=
3
Chlorophyll (spinach extract)
99.86 (0.72)
99.92 (1.01)
2.96 (0.19)
Chlorophyll (Nymphaealotus extract)
99.90 (0.64)
99.95 (0.83)
3.66 (0.09)
Chlorophyll (Acalyphavillicaulis extract)
99.86 (0.97)
99.88 (1.06)
2.42 (0.04)
HCB
nq
90.41 (1.67)
3.61 (0.28)
DDE
nq
89.97 (0.93)
3.44 (0.01)
DDD
nq
91.28 (1.38)
3.29 (0.14)
Mixture
Chlorophyll
99.79 (1.03)
88.94 (0.73)
3.22 (0.36)
HCB
nq
94.52 (1.84)
3.49 (0.92)
DDE
nq
90.26 (1.51)
2.79 (0.02)
DDD
nq
93.08 (1.96)
3.58 (0.16)
Values in parenthesis are % RSD, and nq is for not quantifiable.GCB was able to bind higher quantities of the analytes than the NIP because it has a layered, planar structure which easily flushed with those of the planar pesticides. The NIPs on the other hand have a three-dimensional (3D) highly cross-linked structure with no recognition sites that could allow them to highly bind the pesticides or the chlorophyll. In addition to the imprints within the MIP structure, the high specificity of the prepared MIP to the chlorophyll was thought to be due to the bulkiness of the 3D structure of the chlorophyll locking with the 3D, highly cross-linked MIP structure.


## 3.2.1. Selectivity Experiments

To investigate selectivity, both the planar pesticides and the interfering species (chlorophyll) were exposed to the MIP as well as to GCB as single entities and in a mixture form at optimum conditions. In all cases the MIP did not bind any of the planar pesticides while the percentage of chlorophyll bound was over 99.75% (see Table1). GCB on the other hand did not show any specific selectivity towards any of the analytes as it bound over 88% of each of the planar pesticides as well as the chlorophyll from their prepared standard solutions. It should be noted that the same experiments were performed with the NIP which also exhibited no specific selectivity as all of the analytes were bound just like with GCB. However the percentages bound by the NIP were very low, less than 3.7% in all cases, and as such were considered negligible.Table 1
A Comparison of selectivity of various adsorbents in specifically binding chlorophyll and/or pesticides at optimized conditions.
Analyte/interferent
% bound to MIP
% bound to GCB
% bound to NIP
n
=
3
n
=
3
n
=
3
Chlorophyll (spinach extract)
99.86 (0.72)
99.92 (1.01)
2.96 (0.19)
Chlorophyll (Nymphaealotus extract)
99.90 (0.64)
99.95 (0.83)
3.66 (0.09)
Chlorophyll (Acalyphavillicaulis extract)
99.86 (0.97)
99.88 (1.06)
2.42 (0.04)
HCB
nq
90.41 (1.67)
3.61 (0.28)
DDE
nq
89.97 (0.93)
3.44 (0.01)
DDD
nq
91.28 (1.38)
3.29 (0.14)
Mixture
Chlorophyll
99.79 (1.03)
88.94 (0.73)
3.22 (0.36)
HCB
nq
94.52 (1.84)
3.49 (0.92)
DDE
nq
90.26 (1.51)
2.79 (0.02)
DDD
nq
93.08 (1.96)
3.58 (0.16)
Values in parenthesis are % RSD, and nq is for not quantifiable.GCB was able to bind higher quantities of the analytes than the NIP because it has a layered, planar structure which easily flushed with those of the planar pesticides. The NIPs on the other hand have a three-dimensional (3D) highly cross-linked structure with no recognition sites that could allow them to highly bind the pesticides or the chlorophyll. In addition to the imprints within the MIP structure, the high specificity of the prepared MIP to the chlorophyll was thought to be due to the bulkiness of the 3D structure of the chlorophyll locking with the 3D, highly cross-linked MIP structure.


## 3.3. Effectiveness of Chlorophyll Removal from Spinach Leaves Extract

The initial chlorophyll absorbance of the methanolic, spinach extract was reduced from 0.683 to as low as 0.092 Au after the addition of the MIP. For the traditional medicine extracts there was removal from a chlorophyll absorbance of 0.795 to 0.0897 Au inNymph lotusand 0.649 to 0.0899 Au in Acalypha villicaulis. In all cases, the MIP had significantly removed the interfering chlorophyll to absorbance values far below what is regarded as the interfering chlorophyll which is the absorbance of a 2% (w/v) chlorophyll standard determined to be 0.401 Au (the literature value is 0.399 Au) [1]. This was also marked by the loss of the green characteristic color of the plant extracts to almost colorless solutions after exposure to the MIP powder.


## 4. Conclusion

Based on these preliminary results it can be concluded that a promising, polymeric sorbent, that is, cheaper and with higher selectivity, would soon replace the challenged, expensive, and nonselective GCB in the dispersive SPE kits of QuEChERS. This would result in cheaper, improved, and reliable analytical results. A rough estimation of the cost of this MIP indicates that it would be at least half the price of the GCB (GCB is about $ 50 per gram).



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*Source: 540240-2013-05-21.xml*