|
Five water samples per village (at a
distance of at least ½ Km from each other) were collected through field
staff of Local Govt. at Bahawalpur, Rahim Yar Khan and Multan Districts.
Out of five, one sample was sent to PCRWR. In total 2395 samples were
received by PCRWR instead of 2500. While 106 samples could not be
collected by UNICEF team due to the reason that water of hand pumps or
tube wells was not available in running condition. The sampling details
are given in Table-1.
Table-1 Sample Collection Details for Bahawalpur, Rahim Yar Khan & Multan
Districts
|
Sr.# |
District |
Tehsil |
No. of Union Councils |
Total No. of Samples |
|
1. |
Bahawalpur |
Bahawalpur |
18 |
145 |
|
Hasilpur |
13 |
110 |
|
Khairpur |
7 |
108 |
|
Ahmedpur East |
30 |
184 |
|
Yazman |
17 |
210 |
|
2. |
Rahim Yar Khan |
Sadiqabad |
29 |
298 |
|
Rahim Yar Khan |
39 |
302 |
|
Khanpur |
27 |
262 |
|
Liaqatpur |
24 |
254 |
|
3. |
Multan |
Multan City |
35 |
56 |
|
Multan Saddar |
58 |
282 |
|
Shujaabad |
16 |
80 |
|
Jalalpur Pirwala |
14 |
103 |
|
Total |
327 |
2395 |
|
2.2
Sample Collection and Preservation |
Water samples were collected in ½ liter
polyethylene bottles according to standard methods. A distance of half
kilometer was maintained between the two sampling points. The preservative
(1% concentrated HCl) was used in the samples collected for arsenic
analysis.
Three analytical methods for arsenic
(inorganic) analysis are reported in standard methods. These methods are;
1) Atomic Absorption Spectrometric (AAS) method, 2) Silver
Diethyldithiocarbamate method and 3) Inductive Coupled Plasma (ICP)
Spectrometric method. Atomic Absorption Spectrometer (Hydride Generation
mode) was used for the analysis of arsenic in water samples. All samples
were analysed on HS 55 Mercury/Hydride system, an accessory (AAS, Vario 6
Analytik Jena AG) for the matrix free determination of the hydride forming
elements such as As, Bi, Sb, Se, Sn and Te.
The Hydride technique makes use of fact
that hydrogen liberated in the reaction of the weakly
acidic sample
solutions with sodium boro-hydride which combines with metal ions to form
gaseous hydrides. These are carried to the hot quartz cell by the carrier
gas and decomposed by collision processes in a series of steps, until free
As atoms were obtained.
2.3.1 Equipment and Apparatus
For the analysis of arsenic the Atomic
Absorption Spectrophotometer (AAS Vario 6 Analytik Jena AG),
Mercury/Hydride System HS55 (Analytik Jena AG), and Argon Gas with 99.99%
purity were used.
2.3.2 Reagents and Their Preparation
The following common reagents
were used for the analysis;
-
Sodium borohydride (NaBH4, 98%
purity)
-
Sodium hydroxide, NaOH
-
Hydrochloric Acid (Concentrated 37% HCl)
-
Arsenic Standard (1007
mg/ml,
As in 2% HNO3, BDH)
In order to make reducing solution (Reductant),
15 g sodium borohydride (NaBH4) and 5 g of sodium hydroxide
were dissolved in 500 ml distilled water. This reagent was used as
reducing agent for Arsenic analysis.
2.3.3 Procedure of Analysis
The HS 55 Mercury/Hydride system
consisting of a basic unit and the cell unit was operated and controlled
from PC. Basic unit consists of three accessories. These include batch
module, single channel-peristaltic pump and gas valve box. The gas valve
box supplied argon gas for scavenging and for transporting the metal
hydrides to the system.

Fig.-1:
Mercury Hydride System of Atomic Absorption Spectrophotometer (AAS)
Pressure of the argon gas cylinder was
adjusted at 3-5 bars. After attaining the necessary temperature (950
oC) reducing agent was fed by the peristaltic pump. A 10 ml sample
was taken into reaction cell and 0.8 ml of concentrated HCl was dispensed
into sample and reaction cell was adjusted properly at its place.
Calibration standards of arsenic with concentrations (0,10,20,30,40,50
ppb) and (50,60,70,80,90,100 ppb) were prepared. New method of calibration
was developed using these standards under the operation of software, and
then the method developed was loaded for analysis of actual samples. HS 55
hydride system analyzes the water samples in the following sequences:
-
Pre-wash time
-
Reaction time
-
Rewash time
The detection limit of this
method is 0.1 ppb.

Fig.-2:
Sample Induction in the Reaction Cell of Mercury Hydride System of AAS
|
2.4
Quality Control Measures |
Strict quality control measures were
observed in the laboratory by adopting calibration of instruments with
known standards and reproducibility checks. Instrument was calibrated with
multiple arsenic standards using standard stock solution. The standard
stock solution was certified by BDH laboratory supplies LE 17 4XN England.
According to certificate of analysis, standard was prepared
gravimetrically to contain the elemental concentration of 1007 ppb. The
solution was assayed titrimetrically and also concentration was verified
by Inductive Coupled Plasma Spectrophotometer (ICP). All the glassware
used for preparation of standard solution were acid washed with 1:1 HCl
and rinsed three times with deionized water prior to use. Deionized water
used for analytical work was freshly prepared having EC of >19 Mohm/cm.
Calibration was evaluated by the value of
R2 (Degree of fitness) between concentration and absorbance
i.e. 0.9995356. After calibration, the analysis of all ground water
samples was carried out. During arsenic analysis, a blank and a known
arsenic standard was run after every 10 samples for accuracy assurance.
After every 10 samples, one pre-analyzed sample was rechecked randomly for
reproducibility evaluation. So 10.02% samples were rechecked and results
showed the %age of reproducibility less than 10% which is recognized
internationally within the range of quality control standards. The results
of blank and standards run after every 10 samples are shown at Annexure-I.
Results of reproducible samples are given as Annexure-II.
Top |