LNOTE
Name
Valid Value List
LNOTE NAME Sort descending
LA Confirmatory analysis was past holding time.
RJ Contract limits originate from BP LaMP Technical Requirements
IO Contract limits originate from BP-GCLN Technical Requirements
DV Corr. coef. for Method of Standard Addition is less than 0.995
UF Counts outside acceptable range.
WC Data accepted.
US Data valid based on matrix spike data generated using this sample.
DP Detected at or above the MRL; refer to reports
DNQ Detected, Not Quantified
AW Detection limit increased due to dilution factor
WV Diesel range compounds are significant.
AB Diesel range not reported due to overlap of hydrocarbon range
FS Diesel range organics, as diesel
FR Diesel range organics, calculated as JP-4 jet fuel
UD Diluted sample: method high range exceeded.
PO Dilutions for BOD failed criteria of 1mg/L resid. diss. O
PP Dilutions for BOD failed criteria of 2mg/L diss. O depletion
K Dioxin: Result is an estimated maximum possible concentration.
K1 Dioxin:The conc.of this analyte should be considered an estimate
YC Dissociated ions may elevate this value (Ca+2, SO4-2 etc.)
GP Duplicate analysis not within control limits
WQ Duplicate precision calculation not required, base concentration < 3X MDL
UP Duplicate RPD exceeds limit with results < 5 x RL. Absolute difference is < RL. Data are valid.
XL Elevated detection limits do not meet llimits specified in QAPP.
RE Elevated reporting limits due to limited sample volume
FK EMPC values could be overestimated due to coelution
OM EMPC/NDR Peak detected does not meet ratio criteria (elevated DL)
P EPA Flag - > 25% D for detected concentrations between 2 columns
E EPA Flag - Analyte exceeded the concentration range of the GC/MS
B EPA Flag - Analyte present in the blank and the sample
D EPA Flag - Analytes analyzed at a secondary dilution
U EPA Flag - Compound was analyzed for, but was not detected
R EPA Flag - Data rejected
J EPA Flag - Estimated value
C EPA Flag - Pesticide result confirmed using GC/MS
N EPA Flag - Presumptive evidence of a compound
A EPA Flag - TIC is a suspected aldol-condensation product
FO Est. maximum possible concentration (EMPC)
TY Estimated due to discrepancies meeting analyte-specific QC criteria. Dual Column %Diff over limit.
RG Estimated result. Result is < RL and > or equal to IDL.
YD Excluding barite, Ba SO4.
YE Excluding molybdenum disulfide, MoS2
HE Extract was run through separation method; see case narrative
FP Extractable hydrocarbons
BO Foaming during purge cycle
WX Gasoline range compounds are significant.
WS Gasoline range compounds having broad peaks are significant.Possibly biologically altered gasoline.
FQ Gasoline range organics calculated as JP-4 jet fuel
RS Gasoline/Diesel used as carbon source for degrading bacteria.
FU Heated purge
XB Heavier gasoline range compounds are significant. Possilbly aged gasoline.
AJ Heavier hydrocarbon than diesel
AS Heavier hydrocarbon than gasoline
PS Heavier hydrocarbon than requested fuel
AC Heavier hydrocarbons contributing to diesel range quantitation
OR Heterotrophic bacteria colonies too numerous to count.
BK Hexavalent chromiun not available; total chromium analyzed
XH High bias in QC sample does not affect result since analyte not detected or below reporting limit.
HQ High concentration blank spike recovery out of limits
HO High concentration matrix spike recovery out of limits
MI Hold time compliance not determined; no sample time on COC
QP Holding Time Immediate. Analyzed as close to receipt as possible
EQ Holding time is 28 days by anal. NO3-NO2 on pres. split & sub NO2
CZ Homogeneity could not be readily achieved using routine methods
PT Hydrocarb. in req. fuel range, but doesn't resemble req. fuel
TD Hydrocarbon reported does not match the pattern of Diesel standard
TE Hydrocarbon reported does not match the pattern of Gasoline standard
CN Hydrocarbon response in diesel range but does not resemble diesel
CO Hydrocarbon response in gasoline range but does not resemble gas
XI Hydrocarbon response in motor oil range but does not resemble motor oil.
XJ Hydrocarbon response in Stoddard solvent range but does not resemble Stoddard solvent.
AR Hydrocarbon response is in excess of C10
AH Hydrocarbon response is in excess of C22
AM Hydrocarbon response is in the C12-C22 range
AF Hydrocarbon response is in the C7-C12 range
AP Hydrocarbon response is in the C7-C14 range
AL Hydrocarbon response is in the C8-C12 range
AG Hydrocarbon response is in the C9-C12 range
AQ Hydrocarbon response is in the C9-C14 range
HZ Hydrocarbon result partly due to individ. peak(s) in diesel range
PV Hydrocarbon result partly due to individ. peak(s) in quant. range
FZ Identified by MS only; based on 1:1 response w/ internal stnd.
MD Identity of individual peak(s) confirmed by GCMS
BN Ignites but does not sustain ignition
OK Incubation performed at 35C for 48hrs in plate count agar
QG Individual analyte exceedances allowed per NELAC
CK Initial analysis within holding time but failed QA/QC criteria
ME Initial analysis within holding time but required confirmation
CL Initial analysis within holding time but required dilution
AU Injection precision not met
UK Instrument sensitivity problem.
BS Insufficient sample available to follow standard QC procedures
DU Insufficient sample quantity for matrix spike/dup matrix spike
BT Insufficient sample to perform the analysis
FL Int. std. ion-abundance ratio measured out of accept. range
FD Interferences affect 10% or more of the total PCDD/PCDF peak area
GR Internal standard recovery is outside method recovery limit
TG Ion Ratio outside of limits, value is estimated maximum possible concentration (EMPC).
AA Kerosene range not reported due to overlap of hydrocarbons
UZ Lab Control Sample RPDs outside of limits for several compounds.

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