Dutch pollutant standards

Short description: Environmental pollutant reference values

Dutch Standards are environmental pollutant reference values (i.e., concentrations in environmental media) used in environmental remediation, investigation and cleanup.[1]

Barring a few exceptions, the target values are underpinned by an environmental risk analysis wherever possible and apply to individual substances. In most cases, target values for the various substances are related to a national background concentration that was determined for the Netherlands.

Groundwater target values provide an indication of the benchmark for environmental quality in the long term, assuming that there are negligible risks for the ecosystem. For metals a distinction is made between deep and shallow groundwater. This is because deep and shallow groundwater contain different background concentrations. An arbitrary limit of 10 metres has been adopted. The target values shown below are for 'shallow' groundwater, 0 – 10 m depth.

The soil remediation intervention values indicate when the functional properties of the soil for humans, plants and animals is seriously impaired or threatened. They are representative of the level of contamination above which a serious case of soil contamination is deemed to exist. The target values for soil are adjusted for the organic matter (humus) content and soil fraction <0.2 µm (Lutum \- Latin, meaning "mud" or "clay"). The values below are calculated for a 'Standard Soil' with 10% organic matter and 25% lutum.

A case of environmental contamination is defined as 'serious' if >25 m³ soil or >100 m³ groundwater is contaminated above the intervention value.

The values presented below are from Annex 1, Table 1, "Groundwater target values and soil and groundwater intervention values". In previous versions of the Dutch Standards, target values for soil were also present. However, in the 2009 version, target values for soils have been deleted for all compounds except metals.

Parameter | Soil (mg/kg dry matter) | Groundwater (µg/L)

|
|

| Target value | Intervention value | Target value | Intervention value
I metals[2]
antimony (Sb) | 3.0 | 15 | 0.15 | 20
arsenic (As) | 29.0 | 55.0 | 10 | 60
barium (Ba) | 160 | 625 | 50 | 625
beryllium (Be) | 1.1 | 30 | 0.05 | 15
cadmium (Cd) | 0.8 | 12 | 0.4 | 6
chromium (Cr) | 100.0 | 380 | 1 | 30
cobalt (Co) | 9.0 | 240 | 20 | 100
copper (Cu) | 36.0 | 190 | 15 | 75
nickel (Ni) | 35.0 | 210 | 15 | 75
lead (Pb) | 85.0 | 530 | 15 | 75
mercury (Hg) | 0.3 | 10.0 | 0.05 | 0.3
molybdenum (Mo) | 3.0 | 200 | 5 | 300
silver (Ag) | - | 15 | - | 40
selenium (Se) | 0.7 | 100 | 0.07 | 160
tellurium (Te) | - | 600 | - | 70
thallium (Tl) | 1.0 | 15 | 2 | 7
tin (Sn) | - | 900 | 2.2 | 50
vanadium (V) | 42.0 | 250 | 1.2 | 70
zinc (Zn) | 140 | 720 | 65 | 800
II Other inorganic substances[3]
chloride | - | - | 100 mg/L | \-
cyanide \- free | - | 20 | 5 | 1,500
cyanide - complex | - | 50 | 10 | 1,500
thiocyanate | - | 20 | - | 1,500
III aromatic compounds[4]
benzene | - | 1.1 | 0.2 | 30
ethylbenzene | - | 110 | 4 | 150
toluene | - | 320 | 7 | 1,000
xylenes (sum) | - | 17 | 0.2 | 70
styrene (vinylbenzene) | - | 86 | 6 | 300
phenol | - | 14 | 0.2 | 2,000
cresols (sum) | - | 13 | 0.2 | 200
IV polycyclic aromatic hydrocarbons (PAH)[5]
PAH (sum of 10) | - | 40 | - | \-
naphthalene | - | - | 0.01 | 70
phenanthrene | - | - | 0.003 | 5
anthracene | - | - | 0.0007 | 5
fluoranthene | - | - | 0.003 | 1
chrysene | - | - | 0.003 | 0.2
benz(a)anthracene | - | - | 0.0001 | 0.5
benzo(a)pyrene | - | - | 0.0005 | 0.05
benzo(k)fluoroanthene | - | - | 0.0004 | 0.05
indeno(1,2,3-cd)pyrene | - | - | 0.0004 | 0.05
benzo(ghi)perylene | - | - | 0.0003 | 0.05
V chlorinated hydrocarbons[6]
a. (volatile) hydrocarbons
monochloroethene (vinyl chloride) | - | 0.1 | 0.01 | 5
dichloromethane | - | 3.9 | 0.01 | 1,000
1,1-dichloroethane | - | 15 | 7 | 900
1,2-dichloroethane | - | 6.4 | 7 | 400
1,1-dichloroethene | - | 0.3 | 0.01 | 10
1,2-dichloroethene (sum) | - | 1 | 0.01 | 20
dichloropropanes (sum) | - | 2 | 0.8 | 80
trichloromethane (chloroform) | - | 5.6 | 6 | 400
1,1,1-trichloroethane | - | 15 | 0.01 | 300
1,1,2-trichloroethane | - | 10 | 0.01 | 130
trichloroethene (Tri)  |  | 2.5 | 24 | 500
tetrachloromethane (Tetra) | - | 0.7 | 0.01 | 10
tetrachloroethene (Per) | - | 8.8 | 0.01 | 40
b. chlorobenzenes
monochlorobenzene | - | 15 | 7 | 180
dichlorobenzenes (sum) | - | 19 | 3 | 50
trichlorobenzenes (sum) | - | 11 | 0.01 | 10
tetrachlorobenzenes (sum) | - | 2.2 | 0.01 | 2.5
pentachlorobenzene | - | 6.7 | 0.003 | 1
hexachlorobenzene | - | 2.0 | 0.00009 | 0.5
c. chlorophenols
monochlorophenols (sum) | - | 5.4 | 0.3 | 100
dichlorophenols (sum) | - | 22 | 0.2 | 30
trichlorophenols (sum) | - | 22 | 0.03 | 10
tetrachlorphenols (sum) | - | 21 | 0.1 | 10
pentachlorophenol | - | 12 | 0.04 | 3
d. polychlorinated biphenyls (PCBs)
polychlorinated biphenyl (sum 7) | - | 1 | 0.01 | 0.01
e. other chlorinated hydrocarbons
monochloroanilines (sum) | - | 50 | - | 30
dioxin (sum I-TEQ) | - | 0.00018 | - | N/A
chloronaphthalene (sum) | - | 23 | - | 6
VI pesticides[7]
a. organochlorine pesticides
chlordane (sum) | - | 4 | 0.02 ng/L | 0.2
DDT (sum) | - | 1.7 | - | \-
DDE (sum) | - | 2.3 | - | \-
DDD (sum) | - | 34 | - | \-
DDT/DDE/DDD (sum) | - | - | 0.004 ng/L | 0.01
aldrin | - | 0.32 | 0.009 ng/L | \-
dieldrin | - | - | 0.1 ng/L | \-
endrin | - | - | 0.04 ng/L | \-
drins (sum) | - | 4 | - | 0.1
α-endosulfan | - | 4 | 0.2 ng/L | 5
α-HCH | - | 17 | 33 ng/L | \-
β-HCH | - | 1.6 | 8 ng/L | \-
γ-HCH (Lindane) | - | 1.2 | 9 ng/L | \-
HCH-compounds (sum) | - | - | 0.05 | \-
heptachlor | - | 4 | 0.005 ng/L | 0.3
heptachlor-epoxide (sum) | - | 4 | 0.005 ng/L | 3
b. organophosphorus pesticides
none |  |  |  |
c. organotin pesticides
organotin compounds (sum) | - | 2.5 | 0.05 - 16 ng/L | 0.7
d. chlorophenoxy-acetic acid herbicides
MCPA | - | 4 | 0.02 | 50
e. other pesticides
atrazine | - | 7.1 | 29 ng/L | 150
carbaryl | - | 0.45 | 2 ng/L | 50
carbofuran | - | 0.017 | 9 ng/L | 100
VII Other substances[8]
asbestos | - | 100 | - | \-
cyclohexanone | - | 150 | 0.5 | 15,000
dimethyl phthalate | - | 82 | - | \-
diethyl phthalate | - | 53 | - | \-
diisobutyl phthalate | - | 17 | - | \-
dibutyl phthalate | - | 36 | - | \-
butyl benzyl phthalate | - | 48 | - | \-
dihexyl phthalate | - | 220 | - | \-
di(2-ethylhexyl)phthalate | - | 60 | - | \-
phthalates (sum) | - | - | 0.5 | 5
mineral oil | - | 5,000 | 50 | 600
pyridine | - | 11 | 0.5 | 30
tetrahydrofuran | - | 7 | 0.5 | 300
tetrahydrothiophene | - | 8.8 | 0.5 | 5,000
tetrabromomethane (bromoform) | - | 75 | - | 630

## References

1. ↑ Intervention values 2010[yes|permanent dead link|dead link}}]
2. ↑ Annex 1, Table 1, Section 1
3. ↑ Annex 1, Table 1, Section 2
4. ↑ Annex 1, Table 1, Section 3
5. ↑ Annex 1, Table 1, Section 4
6. ↑ Annex 1, Table 1, Section 5
7. ↑ Annex 1, Table 1, Section 6
8. ↑ Annex 1, Table 1, Section 7

0.00

(0 votes)

Original source: https://en.wikipedia.org/wiki/Dutch pollutant standards. Read more

|

Retrieved from "https://handwiki.org/wiki/index.php?title=Earth:Dutch_pollutant_standards&oldid=1066918"