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Brazilian Journal of Analytical Chemistry - BRJAC - Brazilian Journal ...

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An early approach to PAA determination involves a<br />

two-step titration. The H 2 O 2 present is titrated at a low<br />

temperature with a standard solution <strong>of</strong> potassium permanganate<br />

(KMnO 4 ) in the first step. Potassium iodide<br />

is then rapidly added and the iodine liberated by the<br />

PAA is titrated with a standard thiosulfate solution. This<br />

procedure is called the potassium permanganate – thiosulfate<br />

titration method and has been used as the reference<br />

method for monitoring industrial PAA applications<br />

[6,11,12].<br />

There are other methods to determine PAA in disinfectant<br />

samples [2], in synthetic samples [3], in brewery<br />

cleaning-in-place disinfection processes [4,11,13], in tap<br />

water [6] and in wastewater samples previously treated<br />

with PAA [14] using spectrophotometry [2,4,6,14-16],<br />

potentiometry [3], gas chromatography [17] and highperformance<br />

liquid chromatography [11,13].<br />

An analytical method for the analysis <strong>of</strong> PAA requires<br />

high selectivity and little cross-reaction with the<br />

coexistent H 2 O 2 . The coexistence <strong>of</strong> PAA with H 2 O 2 is<br />

unavoidable owing to the synthesis <strong>of</strong> PAA from H 2 O 2<br />

and acetic acid, as mentioned above, and its continuous<br />

decomposition [3]. A rapid analytical technique is<br />

also desirable for the analysis <strong>of</strong> PAA, since diluted solutions<br />

are unstable and they have to be recalibrated<br />

frequently using titration or other absolute determination<br />

methods [3,11]. But, a rapid analytical technique is<br />

difficult using a manual procedure.<br />

By employing automatic procedures, however, these<br />

goals may be attained using those based on a sequential<br />

injection analysis (SIA) [18] or a multicommuted<br />

flow injection analysis process (MCFIA) [19-21].<br />

Solenoid micro-pumps were introduced to replace<br />

peristaltic pumps as an alternative for fluid propulsion<br />

in a flow system [22]. A flow system based on micropumps<br />

has been designed employing one propelling<br />

device for each solution, controlled by a microcomputer,<br />

thus permitting solution flow rates that can be<br />

individually varied by the s<strong>of</strong>tware [23].<br />

The inherent features <strong>of</strong> the MCFIA, such as versatility,<br />

low reagent consumption, and robustness, are also<br />

enhanced using a solenoid micro-pump to propel sample<br />

and reagent solutions [18, 24-28].<br />

In this work, we describe the development <strong>of</strong> a multicommuted<br />

flow injection procedure for the spectrophotometric<br />

determination <strong>of</strong> peracetic acid in disinfectants<br />

employing solenoid micro-pumps to propel<br />

reagent solutions contained in Vacu-vials ® ampoules<br />

(CHEMetrics, Calverton, VA, U.S.). The detection was<br />

measured at 565 nm.<br />

2. experImental<br />

2.1. safety n o t e<br />

PAA is strong oxidizer, is incompatible with easily oxidized<br />

substances and forms explosive mixtures. These<br />

www.brjac.com.br<br />

Silva et al.<br />

solutions are severely irritating to eyes, skin and mucous<br />

membranes.<br />

2.2. re a g e n t s a n d s o l u t Io n s<br />

All the solutions were prepared from analytical reagent<br />

grade chemicals using ultrapure water (18 MΩ<br />

cm -1 ) obtained by means <strong>of</strong> a Milli-Q (Millipore Corp.,<br />

USA) water purification system.<br />

The PAA solutions were prepared from their stock solutions<br />

(15 %, w/v). The concentration <strong>of</strong> the PAA stock<br />

solution, obtained from Microbiana Descontaminações<br />

Ltda (São Paulo, SP – Brazil), was analyzed to be 169.7<br />

± 2.2 g L -1 using the conventional method proposed by<br />

Greenspan and Mackellar [12]. An aqueous stock solution<br />

<strong>of</strong> 100 mg L -1 peracetic acid was prepared. The concentrations<br />

<strong>of</strong> calibration solutions varied from 0.5 to 5.0<br />

mg L -1 <strong>of</strong> PAA. Sample solutions <strong>of</strong> PAA were prepared<br />

by diluting the appropriate volume <strong>of</strong> PAA with water.<br />

Vacu-vials ® ampoules (CHEMetrics, Calverton, VA,<br />

U.S.) containing approximately 2 mL <strong>of</strong> DDPD solution<br />

were used as the reagent. The DDPD solution is<br />

a methyl-substituted form <strong>of</strong> DPD (N, N-diethyl-p-phenylenediamine)<br />

which is kept in a sealed glass tube under<br />

vacuum.<br />

The activator solution was 15 g L -1 potassium iodide.<br />

Three drops <strong>of</strong> the activator solution were added to 25<br />

mL <strong>of</strong> the calibration and PAA sample solutions.<br />

All disinfectant samples contained peracetic acid (approximately<br />

15%, v/v), acetic acid (16%, v/v) and hydrogen<br />

peroxide (23 %, v/v), although the package label<br />

did not specify a PAA concentration. The disinfectant<br />

samples were diluted to the desired concentration with<br />

water prior to analysis.<br />

fi g u rE 1. fl o w diagram o f thE m u l t iC o m m u t E d f l o w systEm. a) diagram o f<br />

thE f l o w systEm. P 1 , P 2 a n d P 3 : s o l E n o i d m iC r o-PumPs; s: s a m P l E; r: rE a g E n t<br />

s o l u t i o n; C: CarriEr s o l u t i o n (h 2 o), rC: rE a C t i o n C o i l, 0.8 m m i.d., 100<br />

Cm; x: C o n f l u E n C E; dEt: dEtECtor, 565 n m; w: w a s t E. B) sw i tC h t i mE C o u rs E<br />

o f m iC r o-PumPs, rEsPECtivEly t 1 , t 2 a n d t 3 . st: s a m P l i n g stEP; wt: washing<br />

stEP. thE shadow arEas BEnEath o f l i nE s indiCatE that thE s o l E n o i d m iC r o-<br />

PumPs w E r E switChEd on.<br />

159

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