ASSOCIATIONS OF POLYCYCLIC AROMATIC HYDROCARBONS (PAHS) WITH SIZE FRACTIONATED SEDIMENT PARTICLES - PowerPoint PPT Presentation

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ASSOCIATIONS OF POLYCYCLIC AROMATIC HYDROCARBONS (PAHS) WITH SIZE FRACTIONATED SEDIMENT PARTICLES

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ASSOCIATIONS OF POLYCYCLIC AROMATIC HYDROCARBONS (PAHS) WITH SIZE FRACTIONATED SEDIMENT PARTICLES Jejal Reddy Bathi, Geosyntec Consultants, Santa Barbara, CA -93110 – PowerPoint PPT presentation

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Title: ASSOCIATIONS OF POLYCYCLIC AROMATIC HYDROCARBONS (PAHS) WITH SIZE FRACTIONATED SEDIMENT PARTICLES


1
ASSOCIATIONS OF POLYCYCLIC AROMATIC HYDROCARBONS
(PAHS) WITH SIZE FRACTIONATED SEDIMENT PARTICLES
  • Jejal Reddy Bathi, Geosyntec Consultants, Santa
    Barbara, CA -93110
  • Robert Pitt, The University of Alabama,
    Tuscaloosa, AL -35487
  • Shirley Clark, Penn State Harrisburg,
    Middletown, PA-17507

2
ASSOCIATIONS OF PAHS WITH SIZE FRACTIONATED
SEDIMENT PARTICLES
  • Introduction
  • Non-point sources are major contributors of
    PAHs to the environment (US EPA 2000)
  • PAHs predominantly associate with solids (low
    solubility and are hydrophobic)
  • Adsorption on particulate matter is the main
    transport and fate mechanism of PAHs in the
    environment
  • Understanding the distribution of contaminants
    with particle sizes is needed for effective and
    economical treatment of PAHs in runoff
  • Contributing source areas affect the magnitude
    of PAH concentrations with particles (USGS 2003)

3
ASSOCIATIONS OF PAHS WITH SIZE FRACTIONATED
SEDIMENT PARTICLES
  • Sediment Sample Collection and Analyses
  • Sampling Location 1 Cribbs Mill Creek
  • Major Contributing Source Areas Residential Area
  • Samples were collected at the end of a concrete
    channel

4
ASSOCIATIONS OF PAHS WITH SIZE FRACTIONATED
SEDIMENT PARTICLES
  • Sediment Sample Collection and Analyses
  • Sampling Location 2 Hunter Creek
  • Major Contributing Source Areas Commercial
    (especially, Auto Service Area next to the
    sampling location), Road Runoff, Residential
    Trailer Park Areas

5
ASSOCIATIONS OF PAHS WITH SIZE FRACTIONATED
SEDIMENT PARTICLES
  • Sediment Sample Collection and Analyses
  • Sampling Location 3 Carrolls Creek
  • Major Contributing Source Areas Residential and
    Commercial areas
  • Had past history of sanitary sewage
    contamination from SSOs

6
ASSOCIATIONS OF PAHS WITH SIZE FRACTIONATED
SEDIMENT PARTICLES
  • Sediment Sample Collection and Analyses
  • Different particle sizes (lt 45µm to gt2800µm) of
    each creek sediment sample were analyzed
    separately for PAH contamination
  • Large Organic Material (LOM) were separated from
    gt2800 um size fraction for separate analyses
  • All size fractions were analyzed for Material
    Composition and Chemical Oxygen Demand (COD)
  • Sediments were analyzed for PAHs by Thermal
    Desorption (TD) extraction followed by Gas
    Chromotoraphy Mass Spectroscopy (GC-MS)
    detection

7
ASSOCIATIONS OF PAHS WITH SIZE FRACTIONATED
SEDIMENT PARTICLES
  • Particle Size Distribution
  • For all cases, the particles in the size range of
    180 to 355 µm were dominant in the sediments.
    Overall, most of the particles were distributed
    in the size range of 90 to 710 µm.

8
ASSOCIATIONS OF PAHS WITH SIZE FRACTIONATED
SEDIMENT PARTICLES
  • Chemical Oxygen Demand
  • For all cases, sediment CODs showed similar
    distribution
  • The COD values of the gt2800µm (LOM only) was
    1.3 to 1.6E09 mg/kg
  • Median particle size based on COD was about 355µm
    for three creeks

9
ASSOCIATIONS OF PAHS WITH SIZE FRACTIONATED
SEDIMENT PARTICLES
  • Material Composition

Temp. (oC) Material Lost at These Temperatures
up to 104 Moisture
104 - 240 Paper debris
240 - 365 Leaves and grass
365 - 470 Rubber
470 - 550 Asphalt
Above 550 Remaining material is inert
Temperature range of 104 550 C
Temperature Range (ºC) LOM Weight Loss LOM Weight Loss
Temperature Range (ºC) Hunter Carroll's
104 - 240 8.6 20.4
240 - 365 42.5 33.5
365 - 470 28.3 3.9
470 - 550 1.3 0.9
Inert Material 19.2 41.4
Temperature range of 240C 365 C
10
ASSOCIATIONS OF PAHS WITH SIZE FRACTIONATED
SEDIMENT PARTICLES
  • 2-Way ANOVA of PAH Concentrations for Particle
    Size and Location

PAH P Value P Value P Value
PAH Size Location SizeLocation
Naphthalene 0 0.088 0.116
Fluorene 0 0.721 0.481
Phenanthrene 0 0.389 0.043
Anthracene 0 0.032 0.821
Fluranthene 0 0 0
Pyrene 0 0 0
Benzo(a)anthracene 0 0.005 0.002
Chrysene 0 0.004 0
Benzo(b)flouranthrene 0 0.002 0.254
Benzo(a)pyrene 0.004 0.032 0.022
Indeno(1,2,3-cd)pyrene 0 0.284 0.25
Dibenz(a,h)anthracene 0 0.019 0.002
Benzo(ghi)perylene 0 0.041 0.493
11
ASSOCIATIONS OF PAHS WITH SIZE FRACTIONATED
SEDIMENT PARTICLES
  • Effects of Particle Sizes and Location on PAH
    Concentrations

One-Way ANOVA of PAH Concentrations by Particles
Cluster Analyses Cluster analyses of analyte
concentrations showed that gt 2800µm (LOM only)
fractions were separated as a single group
distinct from the other size categories at the
75th percent similarity level for most PAH
compounds for most sites
PAH P Value P Value P Value
PAH Cribbs Mill Creek Hunter Creek Carroll's Creek
Naphthalene 0.324 0.000 0.000
Fluorene 0.000 0.000 0.000
Phenanthrene 0.000 0.000 0.000
Anthracene 0.000 0.000 0.000
Fluoranthrene 0.000 0.000 0.000
Pyrene 0.000 0.000 0.000
Benzo(a)anthracene 0.000 0.000 0.000
Chrysene 0.000 0.001 0.000
Benzo(b)flouranthrene 0.000 0.011 0.000
Benzo(a)pyrene 0.039 0.060 0.000
Indeno(1,2,3-cd)pyrene 0.002 0.437 0.000
Dibenz(a,h)anthracene 0.024 0.010 0.000
Benzo(ghi)perylene 0.004 0.118 0.565
12
Concentrations of PAHs by Particle Sizes
  • The PAH concentrations in the gt2800µm (LOM only)
    fractions were several times higher than for the
    other sample sizes and are not shown

13
Mass of PAHs by Urban Stream Sediment Particle
Sizes
  • Almost all of the stream sediment PAHs are
    associated, by mass, in the intermediate particle
    size fraction (90 to 710 µm), even though this
    size range had the lowest concentrations

14
ASSOCIATIONS OF PAHS WITH SIZE FRACTIONATED
SEDIMENT PARTICLES
  • Effect of Land Use on PAH Pollution
  • Probability Plots and One-Way ANOVA were used to
    compare the PAH concentrations at all three sites

Size Range (µm) Cribbs Mill Creek Hunter Creek Carrolls Creek
lt 45 Phenathrene (Low), Benzo(ghi)perylene (High) Fluoranthrene (High), Pyrene (High) Benzo(a)anthracene (High), Chrysene (High), Benzo(a)pyrene (High), Pyrene (Low), Benzo(a)anthracene (Low), Benzo(b)flouranthrene (Low),
45 - 90 Phenathrene (Low) Fluorene (High), Fluoranthrene (High), Pyrene (High), Benzo(a)anthracene ( High), Chrysene (High), Benzo(b)flouranthrene (High) Benzo(a)anthracene (Low),
90 180 None Naphthalene (Low), Fluoranthrene (High), Pyrene (High) Anthracene (Low), Fluoranthrene (Low)
180 - 355 None Fluoranthrene (High) None
355 - 710 None Fluoranthrene (High) None
710 1400 None None Fluoranthrene (Low)
1400 - 2800 None None Fluoranthrene (Low)
gt 2800 (w/o LOM) None None None
gt 2800 (LOM only) None None None
15
ASSOCIATIONS OF PAHS WITH SIZE FRACTIONATED
SEDIMENT PARTICLES
  • Power Analysis
  • With COVs of 0.5 to 0.7 and 5 samples in each
    category, differences of about 100, and larger,
    can be detected
  • For smaller COVs, it is possible to detect
    smaller differences with same sampling effort
    (e.g. COV of 0.3 and with 5 samples, differences
    of about 40 could be detected)

16
ASSOCIATIONS OF PAHS WITH SIZE FRACTIONATED
SEDIMENT PARTICLES
  • Conclusions
  • The highest PAH concentrations were associated
    with stream sediment samples that had the highest
    organic content
  • Most of the mass of the PAHs were associated with
    the intermediate particle sizes (90 710µm) in
    the stream sediments which were in the greatest
    abundance, even though their PAH concentrations
    were the lowest
  • The site with the highest concentrations of most
    of the PAHs in the stream sediments was affected
    by obvious hydrocarbon contamination from
    adjacent commercial automobile service facilities
  • The one year since the SSO contamination, and
    bed erosion material possibly diluting the
    sediments at Carrolls Creek, likely resulted in
    those samples being less contaminated compared to
    the other creek locations
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