Exposure response function for nitrate and iMetHb: Difference between revisions

From Opasnet
Jump to navigation Jump to search
No edit summary
 
(7 intermediate revisions by 3 users not shown)
Line 1: Line 1:
{{variable}}
{{variable|moderator=Päivi Meriläinen}}


== Scope<br> ==
== Scope<br> ==
Line 5: Line 5:


*European countries
*European countries
*Infants < 6 months of age
*Infants 0-6 months old
*Oral exposure from drinking water via baby food formula or drinking water.
*Oral exposure from drinking water via baby food formula or drinking water.


Line 17: Line 17:
=== Data<br> ===
=== Data<br> ===


Accoding to US EPA IRIS (Integrated Risk Information System) NOAEL for nitrate is 10 mg nitrate-nitrogen/L (1.6 mg/kg/day) and LOAEL is 11-20 mg nitrate-nitrogen/L (1.8-3.2 mg/kg/day). Conversion Factor for nitrate-nitrogen is expressed as the amount of nitrogen within the nitrite molecule commonly shown as mg nitrate-nitrogen/L (1 mg nitrate-nitrogen = 4.4 mg nitrate. The oral Reference Dose (RfD), which is based on the assumption that thresholds exist for certain toxic effects such as cellular necrosis, is 1.6E+0 mg/kg/day. This results in early clinical signs of methemoglobinemia in excess of 10% (0-3 months old infants formula). U.S. EPA has evaluated the noncancer oral data for nitrate and derived a reference dose (RfD) of 1.6 mg/kg-day with 10 % of risk to MetHb.  
Accoding to US EPA IRIS (Integrated Risk Information System) NOAEL for nitrate is 10 mg nitrate-nitrogen/L (1.6 mg/kg/day) and LOAEL is 11-20 mg nitrate-nitrogen/L (1.8-3.2 mg/kg/day). Conversion Factor for nitrate-nitrogen is expressed as the amount of nitrogen within the nitrite molecule commonly shown as mg nitrate-nitrogen/L (1 mg nitrate-nitrogen = 4.4 mg nitrate. The oral Reference Dose (RfD), which is based on the assumption that thresholds exist for certain toxic effects such as cellular necrosis, is 1.6E+0 mg/kg/day. This results in early clinical signs of methemoglobinemia in excess of 10% (0-3 months old infants formula). U.S. EPA has evaluated the noncancer oral data for nitrate and derived a reference dose (RfD) of 1.6 mg/kg-day with 10 % of risk to MetHb. <ref>http://www.epa.gov/NCEA/iris/subst/0076.htm </ref>


http://www.epa.gov/NCEA/iris/subst/0076.htm
The exposure response slope was calculated from the following equation:


1-e ^(x*1.6)= 0.1
x = 0.06585
The main assumptions for ERF slope area when concidering the background referenced are:
<ref>Bosch, H.M., A.B. Rosefield, R. Huston, H.R. Shipman and F.L. Woodward. 1950. Methemoglobinemia and Minnesota well supplies. Journal of American Water Works Association. 42, 161-170. </ref>
<ref>Walton, G. 1951. Survey of literature relating to infant methemoglobinemia due to nitrate-contaminated water. American Journal of Public Health. 41, 986-996. </ref>
<ref>USEPA 2008. Integrated Risk Information System (IRIS). Nitrate search, retrieved from the Internet on 29th of August 2008 http://www.epa.gov/NCEA/iris/subst/0076.htm </ref>
* Oral exposure is well water origin
* Exposured population 0-3 months old infants in North-America in the 1950's
* Exposure route: 0-3 months old infants formula
However, in the nitrate risk assessment the ERF slope factor is applied for a exposure situation excluding well water exposure and extended from 0-6 month old infants exposure orally to both baby food formula and pure drinking water. This may have the most importance in terms of magnitude of results.


=== Formula<br> ===
=== Formula<br> ===


The variable "Exposure response function for nitrate and iMetHb" is found in the Analytica version of the nitrate model.  [[Image:Nitrate.ANA]]


=== Unit<br> ===
=== Unit<br> ===
Line 31: Line 46:
== Result<br> ==
== Result<br> ==


*Slope of exposure response function for nitrate and iMet Hb= 0.06585
 
*Environmental risk level for NO3- =133.7 mg/l
=== References ===
*No observed adverded effect level (NOEL) for nitrate in drinking water= 1.6 mg/kg/d
 
*LOAEL for NO3- = 15,5 mg/l
<references />
*US EPA reference oral dose for nitrate = 7 mg/kg/d
*Acceptable daily intake of NO3- = 3.7 mg/kg/d

Latest revision as of 12:54, 18 November 2009


Scope

To define the exposure response factor for nitrate exposure from drinking water causing iMetHb

  • European countries
  • Infants 0-6 months old
  • Oral exposure from drinking water via baby food formula or drinking water.


Definition

Causality

NA

Data

Accoding to US EPA IRIS (Integrated Risk Information System) NOAEL for nitrate is 10 mg nitrate-nitrogen/L (1.6 mg/kg/day) and LOAEL is 11-20 mg nitrate-nitrogen/L (1.8-3.2 mg/kg/day). Conversion Factor for nitrate-nitrogen is expressed as the amount of nitrogen within the nitrite molecule commonly shown as mg nitrate-nitrogen/L (1 mg nitrate-nitrogen = 4.4 mg nitrate. The oral Reference Dose (RfD), which is based on the assumption that thresholds exist for certain toxic effects such as cellular necrosis, is 1.6E+0 mg/kg/day. This results in early clinical signs of methemoglobinemia in excess of 10% (0-3 months old infants formula). U.S. EPA has evaluated the noncancer oral data for nitrate and derived a reference dose (RfD) of 1.6 mg/kg-day with 10 % of risk to MetHb. [1]

The exposure response slope was calculated from the following equation:

1-e ^(x*1.6)= 0.1

x = 0.06585


The main assumptions for ERF slope area when concidering the background referenced are: [2] [3] [4]

  • Oral exposure is well water origin
  • Exposured population 0-3 months old infants in North-America in the 1950's
  • Exposure route: 0-3 months old infants formula

However, in the nitrate risk assessment the ERF slope factor is applied for a exposure situation excluding well water exposure and extended from 0-6 month old infants exposure orally to both baby food formula and pure drinking water. This may have the most importance in terms of magnitude of results.

Formula

The variable "Exposure response function for nitrate and iMetHb" is found in the Analytica version of the nitrate model. File:Nitrate.ANA

Unit

mg/kg/d / mg/l

Result

References

  1. ↑ http://www.epa.gov/NCEA/iris/subst/0076.htm
  2. ↑ Bosch, H.M., A.B. Rosefield, R. Huston, H.R. Shipman and F.L. Woodward. 1950. Methemoglobinemia and Minnesota well supplies. Journal of American Water Works Association. 42, 161-170.
  3. ↑ Walton, G. 1951. Survey of literature relating to infant methemoglobinemia due to nitrate-contaminated water. American Journal of Public Health. 41, 986-996.
  4. ↑ USEPA 2008. Integrated Risk Information System (IRIS). Nitrate search, retrieved from the Internet on 29th of August 2008 http://www.epa.gov/NCEA/iris/subst/0076.htm
Retrieved from "https://en.opasnet.org/index.php?title=Exposure_response_function_for_nitrate_and_iMetHb&oldid=11987"