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ppm
(grams analyte/grams sample)x10^6
Molarity
moles analyte/liter of solution
Volume Percent
(volume solute/volume soution)x100
Volume ppm
(volume solute/volume solution)x10^6
kilo-
10^3
deci-
10^-1
centi-
10^-2
milli-
10^-3
micro-
10^-6
nano-
10^-9
pico-
10^-12
femto-
10^-15
weight percent
(grams analyte/grams sample)x100
ppt
(grams analyte/grams sample)x10^3
ppt simplified
gram analyte/liter solution
ppm simplified
mg analyte/liter solution
ppb simplified
micrograms analyte/liter solution
pptr simplified
nanograms analyte/liter solution
buoyancy correction
m=(m'(1-(air density/weight density)))/(1-(air density/object density))
accuracy
closeness of the mean to the "true value"
precision
reproducibility of individual measurements
Uncertainty in Addition/Subraction
e=sqrt(ex1^2+ex2^2+ex3^2+...)
Uncertainty in Multiplication/Division
e=y*sqrt((ex1/x1)^2+(ex2/x2)^2+(ex3/x3)^2+...)
Significant Figures in Logarithms and antilogarithms
the number of significant figures in the log should equal the number of digits in the mantissa
How many significant figures in log(205.5)
four significant figures, so you will need four decimal places in your answer
pH
-log[H3O+]
[H3O+]
10^-pH
Absorbance
-log(transmittance)
Random Error
-repeated measurements are sometimes high and sometimes low
-cannot be corrected for
Systematic Error
-repeated measurements are usually always high or always low
-can and should be corrected for
Relative uncertainty=
absolute uncertainty/magnitude of measurement
68% of measurements in a Gaussian Curve will lie
between the mean-1 and the mean+1
Variance in standard deviation
standard deviation squared
mean=
true value +-time*standard deviation
T-test Case 1
measure sample of known composition
T-test case 2
compare replicate measurement of an unknown sample
T-test case 3
compare individual difference of an unknown sample
- two sets of data analyzed by both methods being used
T-test case 1 equation
true value= mean (+-) (time*standard deviation)/sqrt(number of measurements))
T-test case 1 Tcalc=
(sqrt(n)Iknown value-calculated meanI)/standard deviation
For Case 1:
If Tcalc>Ttable
the actual value isn't in the range and it is bad
For Case 1:
If Tcalc
the actual value is close to our calculated value
For Case 2:
you need to first solve for Fcalc=
(larger standard deviation)^2/(smaller standard deviation)^2
If Fcalc
Case 2A
If Fcalc>Ftable, you should use
Case 2B
T-Test Case 2A: Tcalc=
(Icalculated mean 1-calculated mean 2I/spooled)sqrt((n1n2)/(n1+n2))
For Case 2A:
if Tcalc < Ttable, then
the two sets of data are statistically indistinguishable
For Case 2A:
spooled(standard deviation pooled)=
sqrt((s1^2(n1-1)+s2^2(n2-1))/(n1+n2-2))
where s=standard deviation and n=number of measurements
For Case 2B:
Tcalc=
(Icalculated mean 1-calculated mean 2I)/sqrt((s1^2/n1)+(s2^2/n2))
For case 2B:
if Tcalc
the two sets of data are indistinguishable
For Case 3:
Sd=
sqrt((sum of (difference-average difference)^2)/n-1)
For Case 3:
Tcalc=
(Iaverage differenceI/Sd)*sqrt(n)
Q-test
Q=gap/range
For the Q-test, if Qcalculated>Qtable,
the value in question can be rejected with 90% confidence
Grubbs test
Gcalculated= Iquestionable value-calculated meanI/standard deviation
-calculated mean and standard deviation need to include the questionable point
For the Grubbs test, if Gcalculated
you need to keep the questionable point in the set of data
Absorbance corrected for dilution=
Absorbance measured*(total volume/initial volume)
Energy=
Plancks constant*frequency
Planck's constant=
6.626x10^-34 Js
c=(in terms of energy and absorption)
wavelenght*frequency
E=
(planck's constant*c)/wavelength
Beer's Law Equation
Absorbance= constantdistanceconcentration
Transmittance Equation=
P/Po
Po= particular intensity at a specific wavelength
Percent Transmittance=
Transmittance x100
Acid
has a conjugate base and could potentially donate a proton
Base
has a conjugate acid and could potentially gain another proton
what k do you have when you have a base + water on the reactants side?
Kb
what k do you have when you have an acid + water on the reactants side?
Ka
what k do you have when you have a base + water on the products side?
1/Kb
what k do you have when you have an acid + water on the products side?
1/Ka
what is the k equation?
k=products/reactants
- this does not include any solids or liquids, only aqueous solutions
what is the k-value associated with the dissociation of water molecules or 2H20⇌H3O+ + OH-
Kw=1.0x10^-14
Kw=
[H30+][OH-]
Kw= (in terms of other k values)
Ka*Kb
pKw=
pH+pOH
A weak acid consists of a Ka value of
10^-3 or less
Direct Titration
standardized titrant is added to the analyte until the end point is observed
Indirect Titration
includes a back titration, and occurs whenever a direct titration is not feasible
Dilution Factors
M1V1=M2V2
Push the reaction to the products side if you have a
very large K value
Push the reaction to the reactants side if you have a
very small K value
You need to consider the autoprotolysis of water when
the concentration is <10^-5
How to write a charge balance equation
You put all of the positive charges on the left hand side and all of the negative charges on the right hand side. You need to take the number of charges and use it as a coefficient out front.
In Example: NO3^4- : 4[NO3^4-]
How to write a mass balance equation
Concentration of Solution= concentration of both products. If one of the products can add or lose a proton that needs to be included in the equation. *metals and chloride ions do not gain or lose any protons.
Charge Balance Equations
can only have one of these equations per problem
Mass Balance Equations
can have multiple of these equations per problem
when do you use the Henderson-Hasselbalch equation?
when you are dealing with buffers
Henderson-Hasselbalch equation
pH=pKa+log[A-]/[HA]
titrant
the liquid that goes in the buret and what is going down
analyte
unknown that you are trying to figure out
equivalence point
theoretical volume of titrant to completely react with the analyte
end point
experimental volume of titrant needed to completely react with the analyte and determined by a physical change in the solution of the analyte
titration error
difference between equivalence point and end point
primary standard
-typically used to determine concentration of the titrant
-an ideal primary standard would have high purity(99.9%), stable, cheap, relatively high formula weight
standard solution
solution that has known composition
zwitterionic form
an ion that can be an acid or a base
How do you solve polyprotic titrations
if Ka1 is 3 orders of magnitudes larger than Ka2
How do you solve polyprotic titrations for the zwitterionic form of the ion
you use our special tool to solve for [H3O+]
[H3O+] using the special tool equation:
=sqrt((K1K2[HL]+K1Kw)/(K1+[HL]
[H30+] simplified using the special tool equation:
=sqrt(K1K2)
pH using the special tool equation:
=0.5(pK1+pK2)