The function sfCharacteristics()
samples from multiple Pert distributions the
intrinsic and extrinsic characteristics of RTE smoked seafood, which affects microbial growth; namely,
water activity, pH, contents of salt, phenol, nitrites, acetic acid, benzoic acid, citric acid, diacetate,
lactic acid and sorbic acid, and concentration of CO_2
in equilibrium in the package.
Since sampling is carried out at lot level; all the RTE seafood units of a lot have the same characteristics.
Usage
sfCharacteristics(
nLots = data$nLots,
awminSF = NULL,
awmodeSF = NULL,
awmaxSF = NULL,
NaClminSF = 1.5,
NaClmodeSF = 3.4,
NaClmaxSF = 5.3,
PminSF = 5,
PmodeSF = 10,
PmaxSF = 22,
pHminSF = 5.8,
pHmodeSF = 6.1,
pHmaxSF = 6.5,
CO2equilibriumminSF = 0.25,
CO2equilibriummodeSF = 0.25,
CO2equilibriummaxSF = 0.3,
NITminSF = 0,
NITmodeSF = 0,
NITmaxSF = 0,
aaWphminSF = 0,
aaWphmodeSF = 0,
aaWphmaxSF = 0,
baWphminSF = 0,
baWphmodeSF = 0,
baWphmaxSF = 0,
caWphminSF = 0,
caWphmodeSF = 0,
caWphmaxSF = 0,
daWphminSF = 500,
daWphmodeSF = 1500,
daWphmaxSF = 1900,
laWphminSF = 6000,
laWphmodeSF = 12000,
laWphmaxSF = 28000,
saWphminSF = 0,
saWphmodeSF = 0,
saWphmaxSF = 0
)
Arguments
- nLots
Number of lots or size of the Monte Carlo simulation
- awminSF
Minimum water activity of RTE. If null,it will be calculated from NaCl concentration.
- awmodeSF
Mode of water activity of RTE.
- awmaxSF
Maximum water activity of RTE.
- NaClminSF
(%) Minimum NaCl of RTE
- NaClmodeSF
(%) Mode of NaCl of RTE
- NaClmaxSF
(%) Maximum NaCl of RTE
- PminSF
(ppm) Minimum phenol concentration in RTE
- PmodeSF
(ppm) Mode of phenol concentration in RTE
- PmaxSF
(ppm) Maximum phenol concentration in RTE
- pHminSF
Minimum pH of RTE
- pHmodeSF
Mode of pH of RTE
- pHmaxSF
Maximum pH of RTE
- CO2equilibriumminSF
(proportion) Minimum
CO_2
concentration in atmosphere in RTE package (e.g. .0.25)- CO2equilibriummodeSF
(proportion) Mode of
CO_2
concentration in atmosphere in RTE package- CO2equilibriummaxSF
(proportion) Maximum
CO_2
concentration in atmosphere in RTE package- NITminSF
(ppm) Minimum nitrites concentration in RTE
- NITmodeSF
(ppm) Mode of nitrites concentration in RTE
- NITmaxSF
(ppm) Maximum nitrites concentration in RTE
- aaWphminSF
(ppm) Minimum acetic acid concentration in RTE
- aaWphmodeSF
(ppm) Mode of acetic acid concentration in RTE
- aaWphmaxSF
(ppm) Maximum acetic acid concentration in RTE
- baWphminSF
(ppm) Minimum benzoic acid concentration in RTE
- baWphmodeSF
(ppm) Mode benzoic acid concentration in RTE
- baWphmaxSF
(ppm) Maximum benzoic acid concentration in RTE
- caWphminSF
(ppm) Minimum citric acid concentration in RTE
- caWphmodeSF
(ppm) Mode of citric acid concentration in RTE
- caWphmaxSF
(ppm) Maximum citric acid concentration in RTE
- daWphminSF
(ppm) Minimum diacetate concentration in RTE
- daWphmodeSF
(ppm) Mode of diacetate concentration in RTE
- daWphmaxSF
(ppm) Maximum diacetate concentration in RTE
- laWphminSF
(ppm) Minimum lactic acid concentration in RTE
- laWphmodeSF
(ppm) Mode of lactic acid concentration in RTE
- laWphmaxSF
(ppm) Maximum lactic acid concentration in RTE
- saWphminSF
(ppm) Minimum sorbic acid concentration in RTE
- saWphmodeSF
(ppm) Mode of sorbic acid concentration in RTE
- saWphmaxSF
(ppm) Maximum sorbic acid concentration in RTE
Value
A list containing vectors aw
, NaCl
, pH
, P, CO2equi
, NIT
, aaWph
, baWph
,
caWph
, daWph
, laWph
, saWph
to be used in the growth functions sfMejlholmDalgaard()
and
sfMejlholmDalgaardLAB()
for estimating specific growth rates of L. monocytogenes and lactic
acid bacteria, respectively, in RTE seafood.
Note
All parameters end with SF
not to be confounded with growth parameters. If parameters for water activity aw
are NULL
,
aw
will be evaluated from NaCl concentration in the growth functions. The default parameters of the Pert distributions describing
variability in pH
, contents of salt
, phenol
, diacetate
, lactic acid
, and concentration of CO_2
in equilibrium for smoked seafood,
were taken from WHO (2022)
(Table 3.25) and Pérez-Rodríguez (2017)
.
References
WHO (2022). “A Roadmap for the Development of Risk Assessment Models of Listeria monocytogenes in Selected Produce and Seafood Products.” World Health Organization. Pérez-Rodríguez FCEBSJAVA (2017). “Closing gaps for performing a risk assessment on Listeria monocytogenes in ready-to-eat (RTE) foods: activity 2, a quantitative risk characterization on L. monocytogenes in RTE foods; starting from the retail stage.” EFSA Supporting publication 2017:EN-1252. Pouillot R, Delignette-Muller M (2010). “Evaluating variability and uncertainty in microbial quantitative risk assessment using two R packages.” International Journal of Food Microbiology, 142(3), 330-40.
Author
Regis Pouillot rpouillot.work@gmail.com
Examples
N <- matrix(round(10^rnorm(100 * 100, 0, 3)),
ncol = 100, nrow = 100
)
dat <- list(N = N, nLots = 1000)
dat <- sfCharacteristics(dat)
str(dat)
#> List of 12
#> $ aw : NULL
#> $ NaCl : num [1:2] 2.18 2.18
#> $ pH : num [1:2] 6.09 5.95
#> $ P : num [1:2] 15.5 12.7
#> $ CO2equi: num [1:2] 0.275 0.264
#> $ NIT : num [1:2] 0 0
#> $ aaWph : num [1:2] 0 0
#> $ baWph : num [1:2] 0 0
#> $ caWph : num [1:2] 0 0
#> $ daWph : num [1:2] 1111 1557
#> $ laWph : num [1:2] 13473 10225
#> $ saWph : num [1:2] 0 0