Introduction
The Bromide Ion-Selective Electrode has a solid-state crystal membrane. The electrode is designed for the detection of bromide ions (Br^- ) in aqueous solutions and is suitable for use in both field and laboratory applications.
The Bromide Ion is a monovalent anion.
One mole of ( Br-) has a mass of 79.904 grams; 1000ppm is 0.0125M
Dissolve 1.489g anhydrous potassium bromide (KBr) in 1 Litre water.

Physical Specifications
Length of body excluding gold contacts = 130 mm
Length of body including gold contacts = 140 mm
Diameter of body = 8 mm
DC resistance at 25°C < 2.5 MOhm
Minimum feasible sample volume = 5mls

Chemical / Operational Specifications
Preconditioning/ Standard solution : Normally 1000ppm Br- as KBr
(But see General Operating Instructions )
Preconditioning time : 5 minutes
Optimum pH range : pH 1 to pH 12
Temperature range : 0 to 80°C
Recommended ISAB : 5M NaNO3 (Add 2% v/v)
Recommended reference electrode : double junction ( ELIT 002 or 003)
Reference electrode outer filling solution : 0.1M KNO3 or 0.1M CH3COOLi
Electrode slope at 25°C : 54 ± 5 mV/decade
Concentration range : 0.4 to 8,000 ppm (5x10-6 to 0.1 Molar)
Response time : < 10 seconds
Defined as time to complete 90% of the change in potential after immersion in the new solution.
Time for stable reading after immersion : < 1 to > 5 minutes
Depending on concentration, use of ISAB, nature of sample and stabilisation time of liquid junction potential of reference electrode.
Potential drift (in 1000 ppm) : < 3 mV/day (8 hours)
Measured at constant temperature and with ISE and Reference Electrode continually immersed

Interference:
NB: All poly-crystalline membranes contain Silver Sulphide and thus will not give reliable readings if Ag or S ions are present in the solution. The Bromide ISE also has very strong interference from any Cyanide or Iodide in the solution and these ions should be absent or only present in insignificant concentrations. There is also a small interference from Chloride (Selectivity Coefficient ~0.002) and Hydroxyl (0.00003).
The SC is the approximate apparent increase in the measured concentration caused by 1 unit of the interferent.  Thus the likely effect of any interfering ion (% increase) can be calculated as follows: 
        ((expected concentration) x (SC) / (expected Br concentration)) x 100.

Cyanide and Sulphide can be removed by the addition of 1 ml of 0.1 Molar nickel sulphate per 100 ml of sample. Note that this must also be added to all standards as well as samples in order to ensure the same dilution factor and similar matrix.

Follow the instructions in the General Operating Instructions to measure these standard solutions and prepare a calibration graph.

For low ionic strength samples, no sample preparation is necessary. Simply take approximately 50 to 100 mls of sample in a plastic beaker, or even immerse the electrodes directly in a lake or river (but take care to avoid losing the electrodes!). For high ionic strength samples, take 100mls of sample and add 2 mls of buffer solution and stir well before measurement.

Follow the instructions in the electrode operating instructions to measure a series of samples and record the results. Briefly, it is important to note that, if measuring in beakers, the electrodes must be washed and dried between each sample, to avoid cross contamination, and sufficient time must be allowed (2 or 3 minutes), before taking a reading after immersion, to permit the electrode signal to reach a stable value. For the highest precision, frequent recalibration is recommended (see operating instructions).

The results will be displayed as ppm and mol/l. If buffer solution has been added equally to standards and samples then these figures will not need adjusting because they will all be affected by the same dilution factor.