Processing kodak motion picture films, module 3 analytical procedures
Processing kodak motion picture films, module 3 analytical procedures Processing kodak motion picture films, module 3 analytical procedures
CALCULATIONS For K 4 Fe(CN) 6 ; g/L K4Fe(CN) 6 3H2O = (mL sulfato cerate) (N sulfato cerate) (eq. wt. K4Fe(CN) 6 3H2O) (1000) (mL sample) (1000) where: mL sulfato cerate = N = If mL 0.0500 N sulfato cerate = 16.41 mLs; Figure 1 S-shaped Curves volume of sulfato cerate in milliliters required to reach the equivalence point normality of sulfato cerate in milliequivalents per milliliter (meq/mL) equivalent weight of ferrocyanide in eq. wt. = milligrams per milliequivalents [422.41 for K4Fe(CN) 6 3H2O] 1000 = factor to convert milligrams to grams of ferrocyanide mL sample = milliliters of sample pipetted in step 1 of the Treatment of Sample 1000 = factor to convert mLs of sample to liters g/L K 4Fe(CN) 6 3H 2O = g/L K 4Fe(CN) 6 3H 2O = 6.93 800 + 700 (16.41 (0.0500) (422.41) (1000) (50.0) (1000) MiliVolts 600 − 5 4 3 2 1 MiliLiters F002_1122GC 4 Processing KODAK Motion Picture Films, Module 3, Analytical Procedures H24.03
Spectrophotometric Determination of Ferrocyanide in Effluents ECN-0025-1 INTRODUCTION This method is used to determine the concentration of ferrocyanide ion in photoprocessing solution effluents. The ion concentration is determined spectrophotometrically. The sample is diluted, if necessary, such that the ferrocyanide ion [Fe(CN) 6 4-] concentration falls within a range of 0.5 to 5 mg/ L. Results are reported as mg/L of potassium ferrocyanide trihydrate [K 4 Fe(CN) 6 3H 2 O]. A dilution of 25 mL of effluent to 250 mL is sufficient for samples as high as 100 mg/L K 4 Fe(CN) 6 3H 2 O concentration. In most cases, this is adequate. However, this method can be used for samples of potassium ferrocyanide trihydrate concentrations as high as one g/L by making a second dilution of 25 mL to 250 mL. After dilution, the sample is made alkaline to dissolve ferrocyanide. The sample is then filtered to remove any insolubles. The filtrate is acidified and ferrous/ferric reagent added. After 15 minutes, the intensity of the blue color produced is measured at 700 nm using a spectrophotometer equipped with a tungsten lamp. Use of this method requires handling potentially hazardous chemicals. Material Safety Data Sheets (MSDS) should be consulted for each chemical before use. These can be obtained from each chemical supplier. Sample PRECISION AND BIAS A. Repeatability Standard Deviation, 1sr and 95 Percent Confidence Estimate (not including Bias) Repeatability standard deviation is an estimate of the variability one trained analyst should be able to obtain under favorable conditions (analyzing a sample, with one instrument, within one day). The 95 percent confidence estimate (calculated using the repeatability standard deviation) around a single test result will include the mean value 95 percent of the time. To obtain the repeatability data, a single skilled analyst performed five (5) replicates on each of the following solutions during methods development. 1. An effluent sample analyzed as received, at 6.85 mg/L K4Fe(CN) 6 3H2O. 2. The same effluent sample as in number 1, above, reanalyzed after making an analytically weighed, standard addition of 2.36 mg/L K4Fe(CN) 6 3H2O. Potassium Ferrocyanide, trihydrate Mean mg/L K 4Fe(CN) 6 3H 2O Bias Bias is a statistically significant deviation of the mean from the known mix level at a 95 percent confidence level. It is determined for fresh samples only. Bias was not determined for this sample because the component concentration level was not determined independently of the test method. Bias was not determined, since this is an effluent sample with an unknown level of potassium ferrocyanide trihydrate. Recovery Recovery is used for seasoned samples, since the component concentration level was not determined independently of the test method. It is defined as the calculated mean for the seasoned sample with a standard addition of the component minus the mean for the seasoned sample, divided by the actual amount of the standard addition. It is expressed as a percentage. Statistically the recovery of 108.05 percent was significantly different from 100 percent at the 95 percent confidence level, but was judged not to be practically significant. Processing KODAK Motion Picture Films, Module 3, Analytical Procedures H24.03 1 N Repeatability Standard Deviation, 1s r mg/L K 4Fe(CN) 6 3H 2O 95 Percent Confidence Estimate mg/L K 4Fe(CN) 6 3H 2O Effluent Effluent 6.85 5 0.123 ± 0.34 plus Standard Addition 9.40 5 0.105 ± 0.29
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- Page 39 and 40: CALCULATIONS For Na3Fe(CN) 6 g/L Na
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Spectrophotometric Determination of Ferrocyanide in Effluents<br />
ECN-0025-1<br />
INTRODUCTION<br />
This method is used to determine the concentration of<br />
ferrocyanide ion in photoprocessing solution effluents. The<br />
ion concentration is determined spectrophotometrically. The<br />
sample is diluted, if necessary, such that the ferrocyanide ion<br />
[Fe(CN) 6 4-] concentration falls within a range of 0.5 to 5 mg/<br />
L. Results are reported as mg/L of potassium ferrocyanide<br />
trihydrate [K 4 Fe(CN) 6 3H 2 O]. A dilution of 25 mL of<br />
effluent to 250 mL is sufficient for samples as high as<br />
100 mg/L K 4 Fe(CN) 6 3H 2 O concentration. In most cases,<br />
this is adequate. However, this method can be used for<br />
samples of potassium ferrocyanide trihydrate concentrations<br />
as high as one g/L by making a second dilution of 25 mL to<br />
250 mL.<br />
After dilution, the sample is made alkaline to dissolve<br />
ferrocyanide. The sample is then filtered to remove any<br />
insolubles. The filtrate is acidified and ferrous/ferric reagent<br />
added. After 15 minutes, the intensity of the blue color<br />
produced is measured at 700 nm using a spectrophotometer<br />
equipped with a tungsten lamp.<br />
Use of this method requires handling potentially<br />
hazardous chemicals. Material Safety Data Sheets<br />
(MSDS) should be consulted for each chemical before<br />
use. These can be obtained from each chemical supplier.<br />
Sample<br />
PRECISION AND BIAS<br />
A. Repeatability Standard Deviation, 1sr and<br />
95 Percent Confidence Estimate (not including<br />
Bias)<br />
Repeatability standard deviation is an estimate of the<br />
variability one trained analyst should be able to obtain under<br />
favorable conditions (analyzing a sample, with one<br />
instrument, within one day).<br />
The 95 percent confidence estimate (calculated using the<br />
repeatability standard deviation) around a single test result<br />
will include the mean value 95 percent of the time.<br />
To obtain the repeatability data, a single skilled analyst<br />
performed five (5) replicates on each of the following<br />
solutions during methods development.<br />
1. An effluent sample analyzed as received, at 6.85 mg/L<br />
K4Fe(CN) 6 3H2O. 2. The same effluent sample as in number 1, above,<br />
reanalyzed after making an <strong>analytical</strong>ly weighed,<br />
standard addition of 2.36 mg/L K4Fe(CN) 6 3H2O. Potassium Ferrocyanide, trihydrate<br />
Mean<br />
mg/L<br />
K 4Fe(CN) 6 3H 2O<br />
Bias<br />
Bias is a statistically significant deviation of the mean from<br />
the known mix level at a 95 percent confidence level. It is<br />
determined for fresh samples only. Bias was not determined<br />
for this sample because the component concentration level<br />
was not determined independently of the test method.<br />
Bias was not determined, since this is an effluent sample<br />
with an unknown level of potassium ferrocyanide trihydrate.<br />
Recovery<br />
Recovery is used for seasoned samples, since the component<br />
concentration level was not determined independently of the<br />
test method. It is defined as the calculated mean for the<br />
seasoned sample with a standard addition of the component<br />
minus the mean for the seasoned sample, divided by the<br />
actual amount of the standard addition. It is expressed as a<br />
percentage.<br />
Statistically the recovery of 108.05 percent was<br />
significantly different from 100 percent at the 95 percent<br />
confidence level, but was judged not to be practically<br />
significant.<br />
<strong>Processing</strong> KODAK Motion Picture Films, Module 3, Analytical Procedures H24.03 1<br />
N<br />
Repeatability<br />
Standard<br />
Deviation, 1s r<br />
mg/L<br />
K 4Fe(CN) 6 3H 2O<br />
95 Percent<br />
Confidence<br />
Estimate<br />
mg/L<br />
K 4Fe(CN) 6 3H 2O<br />
Effluent<br />
Effluent<br />
6.85 5 0.123 ± 0.34<br />
plus<br />
Standard<br />
Addition<br />
9.40 5 0.105 ± 0.29