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The Effects of Road Transport on Freshwater and Marine Ecosystems

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38<br />

by ARC (1994) indicated that TPH c<strong>on</strong>centrati<strong>on</strong>s ranged from 1,000 up to about 4,000 mg/kg in the<br />

different particle sizes examined<br />

Williams<strong>on</strong> (unpublished data in NIWA 1996) measured PAH c<strong>on</strong>centrati<strong>on</strong>s in suspended sediment<br />

from Hillcrest (Hamilt<strong>on</strong>) <str<strong>on</strong>g>of</str<strong>on</strong>g> 52 - 2,375 µg/kg. Hickey et al. (1997) examined PAH c<strong>on</strong>centrati<strong>on</strong>s in<br />

suspended stormwater particulates from Mt Albert in Auckl<strong>and</strong>. <str<strong>on</strong>g>The</str<strong>on</strong>g> results indicated a total PAH<br />

c<strong>on</strong>centrati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> 972 µg/kg. Data for a total <str<strong>on</strong>g>of</str<strong>on</strong>g> 24 PAHs was reported ranging from 0.2 µg/kg for<br />

napthalene, to 66 µg/kg for benzo(a)pyrene to 126 µg/kg for pyrene <strong>and</strong> 148 µg/kg for<br />

benzo(ghi)perylene.<br />

Stormwater from roads c<strong>on</strong>tains a wide range <str<strong>on</strong>g>of</str<strong>on</strong>g> organic compounds. Many c<strong>on</strong>taminants are present<br />

as a result <str<strong>on</strong>g>of</str<strong>on</strong>g> their emissi<strong>on</strong> from a number <str<strong>on</strong>g>of</str<strong>on</strong>g> sources associated with motor vehicles (e.g., tyre <strong>and</strong><br />

brake pad wear, exhaust emissi<strong>on</strong>). Compounds present <strong>on</strong> road surfaces <strong>and</strong> in stormwater include<br />

volatile organic compounds <strong>and</strong> a wide range <str<strong>on</strong>g>of</str<strong>on</strong>g> semi-volatile organic compounds. <str<strong>on</strong>g>The</str<strong>on</strong>g> PAHs are the<br />

most well understood group <str<strong>on</strong>g>of</str<strong>on</strong>g> SVOCs <strong>and</strong> have been measured in stormwater.<br />

<str<strong>on</strong>g>The</str<strong>on</strong>g> amount <str<strong>on</strong>g>of</str<strong>on</strong>g> any particular organic compound present in the dissolved phase is dependent up<strong>on</strong> its<br />

properties. A higher proporti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> the c<strong>on</strong>centrati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> low MW PAHs is present in the dissolved<br />

phase compared to high MW PAHs which are almost entirely present in the particulate phase.<br />

4.5 Other C<strong>on</strong>stituents<br />

Other C<strong>on</strong>stituents in Particulate Matter<br />

<str<strong>on</strong>g>The</str<strong>on</strong>g> particulate matter transported by stormwater carries a range <str<strong>on</strong>g>of</str<strong>on</strong>g> other c<strong>on</strong>stituents other than<br />

metals <strong>and</strong> organic compounds. <str<strong>on</strong>g>The</str<strong>on</strong>g>se other c<strong>on</strong>stituents include nutrients <strong>and</strong> oxygen dem<strong>and</strong>ing<br />

substances. ARC (1992, 1994) carried out an examinati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> the c<strong>on</strong>centrati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> nutrients <strong>and</strong> their<br />

c<strong>on</strong>stituents in the particulate matter transported from a residential catchment in Auckl<strong>and</strong>.<br />

Organic carb<strong>on</strong> c<strong>on</strong>centrati<strong>on</strong>s in suspended solids in stormwater were found to be higher than those<br />

measured in street gutter dusts (probably due to differential sorting <str<strong>on</strong>g>of</str<strong>on</strong>g> organic suspended solids).<br />

C<strong>on</strong>centrati<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> up to 22% organic carb<strong>on</strong> were measured. Density separati<strong>on</strong> may result in the<br />

increase in c<strong>on</strong>centrati<strong>on</strong> compared to the source. Increases were also noted in relati<strong>on</strong> to total<br />

Kjeldahl nitrogen (TKN) with c<strong>on</strong>centrati<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> up to 0.09% being measured. In relati<strong>on</strong> to both OC<br />

<strong>and</strong> TKN, no assessment <str<strong>on</strong>g>of</str<strong>on</strong>g> the relative c<strong>on</strong>tributi<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> road transport to both c<strong>on</strong>stituents (from<br />

hydrocarb<strong>on</strong> <strong>and</strong> NOx emissi<strong>on</strong>s) has been identified. However, although it has been assumed to be<br />

low, the relative c<strong>on</strong>tributi<strong>on</strong> between road transport <strong>and</strong> urban l<strong>and</strong>scape <strong>and</strong> other sources is<br />

expected to be highly variable.<br />

ARC (1992) examined the phosphorus c<strong>on</strong>tent <str<strong>on</strong>g>of</str<strong>on</strong>g> particulates in stormwater from residential <strong>and</strong><br />

commercial catchments in Auckl<strong>and</strong>. <str<strong>on</strong>g>The</str<strong>on</strong>g> results showed that although total phosphorus<br />

c<strong>on</strong>centrati<strong>on</strong>s were high (typically >2,000 mg/kg), the available fracti<strong>on</strong> was a very small part<br />

(typically 2%). C<strong>on</strong>centrati<strong>on</strong>s in that study appeared to be greater than would be expected in local<br />

soils (e.g.,

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