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Table 2 Total concentrations of PAHs plants (ng/g dry wt.) in (sub)urban areas and in the vicinity of human (industrial) activities (after Bakker et al. 2000)

From: Monitoring of environmental exposure to polycyclic aromatic hydrocarbons: a review

Location

Number of PAH’s

Plant

∑PAH concentration in plant (ng g dry wt.)

Reference

Highway (S)

16

Lettuce

17–90

Larssen and Sahlberg (1982)

Highway (CAN)

17

Onionsa, beeta, tomatoesa

10–1,900b

Wang and Meresz (1982)

Al smelter (S)

16

Lettuce

320–920

Larsen and Sahlberg (1982)

Highway (S)

16

Kale

500 (at 50 m)b

5,000(at 10 m)b

Brorström-Lunden and Skärby (1984)

Busy city street (S)

16

Kale

5,000(at 50 m)b

14,000(at 10 m)b

Brorström-Lunden and Skärby (1984)

Urban (USA)

10

Pine

800–1,600

Simonich and Hites (1994)

Urban (USA)

10

sugar maple

500–1,100

Simonich and Hites (1994)

Urban (I)

10

Bay treea

73–880

Lodovici et al. (1994)

Suburban (UK)

16

Pine

20–3,100c

Tremolada et al. (1996)

Suburban (USA)

18

Maple

510 ± 100

Wagrowski and Hites (1997)

Urban (USA)

18

Maple

1600 ± 210

Wagrowski and Hites (1997)

Urban (RBD)

13

Kale

1,000–5,000

Franzaring (1997)

Urban (UK)

16

Grass

153 ± 8

Meharg et a.l (1998)

Polyprop.fire (UK)

16

Grass

2,400d

Meharg et al. (1998)

Industrial (GR)

16

Various vegetablesa

25–239

Kipopoulou et al. (1999)

  1. aWashed leaves
  2. bOriginal concentrations expressed in μg g fresh wt. converted to μg/g dry wt. assuming a fresh wt. dry wt. of 10
  3. cConcentration correlated to number of inhabitants
  4. dHighest concentration