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Survey of the Mercury Content Survey of the Mercury Content of Earthworms on the South of Earthworms on the South River Floodplain River Floodplain John Cianchetti and Dean Cocking, James Madison University, Harrisonburg, VA Bill Berti, DuPont Co., Central Research and Development, Newark, DE South River Science Team April 8, 2008

Survey of the Mercury Content of Earthworms on the South River Floodplain

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Survey of the Mercury Content of Earthworms on the South River Floodplain. John Cianchetti and Dean Cocking, James Madison University, Harrisonburg, VA Bill Berti, DuPont Co., Central Research and Development, Newark, DE South River Science Team April 8, 2008. Objectives of Study. - PowerPoint PPT Presentation

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Page 1: Survey of the Mercury Content of Earthworms on the South River Floodplain

Survey of the Mercury Content of Survey of the Mercury Content of Earthworms on the South River Earthworms on the South River

FloodplainFloodplain

John Cianchetti and Dean Cocking, James Madison University, Harrisonburg, VA

Bill Berti, DuPont Co., Central Research and Development, Newark, DE

South River Science Team April 8, 2008

Page 2: Survey of the Mercury Content of Earthworms on the South River Floodplain

2

Objectives of Study

Conduct a survey of Hg concentrations in earthworms to understand the extent to which mercury bioaccumulates in earthworms.

Evaluate the relationship between total mercury (THg) and methyl mercury (MeHg) concentrations in earthworm and paired soil samples.

Page 3: Survey of the Mercury Content of Earthworms on the South River Floodplain

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Floodplain Earthworm Sample Locations

Grand Caverns

Abbee Road Bridge

Confluence

Ridgeview Pk

North Pk

Crimora

Hopeman Pkwy

Robert Turk Rd

Belvidere Rd

Forestry Ctr

Dooms

Basic Pk

CNF

GGC

BVD

FOR

CRM

RTR

DMS

HPK

BPK

NPK

ARB

RVPPoint sourcePoint source

Waynesboro

Staunton

Control site

Page 4: Survey of the Mercury Content of Earthworms on the South River Floodplain

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Sample collection procedure

A 10x10 square meter grid was established in each location and was subdivided into 1x1m quadrats

5 of the quadrats were randomly selected for sampling.

DuPont
Has this changed appreciably?
Page 5: Survey of the Mercury Content of Earthworms on the South River Floodplain

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Sample collection procedure

Excavated a surface layer of 50 cm at each quadrat to collect minimum of 30 individual earthworms.

Soil samples were collected from this surface layer at each quadrat.

The aliquots from each quadrat were homogenized within a plastic bag and placed in vials for total and methyl mercury analysis; five composite samples per location corresponding to each earthworm sample.

Residual soil from each quadrat was combined to create a composite sample at each location sample used for soil property characterization.

DuPont
Has this changed appreciably?
Page 6: Survey of the Mercury Content of Earthworms on the South River Floodplain

6

Sample Processing: Earthworms

The earthworms were transported to the laboratory in a cooler.

Earthworm samples were sequentially rinsed with DI water in a series of six pyrex glass dishes.

A sub sample of at least 12 earthworms from three quadrats from each location were processed as undepurated samples which were frozen immediately.

A similar sized sample from each quadrat was depurated for 24 hours in a container with moist filter paper, and then frozen.

All samples were shipped to Studio Geochemica for analysis

Page 7: Survey of the Mercury Content of Earthworms on the South River Floodplain

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Summary Earthworm and Soil Sampling Design at Each Location

Quadrat No. Earthworms Soil

Total Hg MeHg

Un-

deparated† De-

parated Un-

deparated† De-

parated† Total Hg MeHg† XAS‡

Soil test§

1 1 1 1 1 1 1 0.2 2 1 1 0.2 3 1 1 1 1 1 1 1 0.2 4 1 1 0.2 5 1 1 1 1 1 1 0.2

Total samples/location 3 5 3 3 5 3 1 1

† Specific quadrat samples for analysis will be randomly selected. ‡ X-ray Absorption Spectroscopy § A composite sample with soil from the quadrats.

All Samples were shipped to Studio Geochemica for analysis

Page 8: Survey of the Mercury Content of Earthworms on the South River Floodplain

8

Detection Limits

With the exception of methyl mercury in earthworms at the control site, analyzed samples all had values well above minimum detection limit (MDL) and the practical quantitative limit (PQL) for the fresh weight samples. (Provided by Studio Geochemica)

Page 9: Survey of the Mercury Content of Earthworms on the South River Floodplain

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0.1

1

10

100

1000

10000

100000

-10 0 10 20 30 40 50

Me

rcu

ry (

ng

/g)

Thg (Wet Weight Basis)THg (Dry Weight Basis)MeHg (Wet Weight Basis)MeHg (Dry Weight Basis)

RVP ARB NPK BPK HPK DMS RTR CRM FOR BVD GGC CNF

Downstream River Kilometer (0 = Waynesboro Point Source)

Mean Total Mercury (THg) and Methyl Mercury (MeHg) in Soil of the South River, VA, Floodplain

± 1 SEM

Page 10: Survey of the Mercury Content of Earthworms on the South River Floodplain

10

1

10

100

1000

10000

100000

-10 0 10 20 30 40 50

Mer

cury

(n

g/g

)Thg (Wet Weight Basis)Thg (Dry Weight Basis)Mehg (Wet Weight Basis)Mehg (Dry Weight Basis)

RVP ARB NPK BPK HPK DMS RTR CRM FOR BVD GGC CNF

Downstream River Kilometer (0 = Waynesboro Point Source)

Mean Mercury (THg & MeHg) in Depurated Earthworms Living on the South River, VA, Floodplain

± 1 SEM

Page 11: Survey of the Mercury Content of Earthworms on the South River Floodplain

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1

10

100

1000

10000

-10 0 10 20 30 40 50

Me

rcu

ry (

ng

/g w

w)

THg (Depurated Earthworms)THg (Undepurated Earthworms)MeHg (Depurated Earthworms) MeHg (Undepurated Earthworms)

Downstream River Kilometer (0 = Waynesboro Point Source)

RVP ARB NPK BPK HPK DMS RTR CRM FOR BVD GGC CNF

A Comparison of THg and MeHg Concentrations in Earthworms Living on the South River, VA, Floodplain

Wet Weight Basis (ww) ± 1 SEM

Page 12: Survey of the Mercury Content of Earthworms on the South River Floodplain

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0

5000

10000

15000

20000

25000

30000

-5 0 5 10 15 20 25 30 35 40 45

To

tal

Mer

cury

(n

g/g

)

Wet Weight Basis (ww)

THg in Soil of the South River, VA, Floodplain

RVP ARB NPK BPK HPK DMS RTR CRM FOR BVD GGC CNF

Downstream River Kilometer (0 = Waynesboro Point Source)

Page 13: Survey of the Mercury Content of Earthworms on the South River Floodplain

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0

5000

10000

15000

20000

25000

-5 0 5 10 15 20 25 30 35 40 45

Mea

n T

ota

l M

ercu

ry (

ng

/g w

w) Wet Weight Basis (ww) ±

1 SEM

Mean THg in Soil of the South River, VA, Floodplain

Downstream River Kilometer (0 = Waynesboro Point Source)

RVP ARB NPK BPK HPK DMS RTR CRM FOR BVD GGC CNF

Page 14: Survey of the Mercury Content of Earthworms on the South River Floodplain

14

0

500

1000

1500

2000

2500

3000

3500

4000

-5 0 5 10 15 20 25 30 35 40 45

Mea

n T

ota

l H

g (

ng

/g w

w)

Mean THg in Depurated Earthworms Living on the South River, VA, Floodplain

Downstream River Kilometer (0 = Waynesboro Point Source)

RVP ARB NPK BPK HPK DMS RTR CRM FOR BVD GGC CNF

Wet Weight Basis (ww) ± 1 SEM

Page 15: Survey of the Mercury Content of Earthworms on the South River Floodplain

15

0

2

4

6

8

10

12

14

-5 0 5 10 15 20 25 30 35 40 45

Mea

n M

eth

yl M

ercu

ry (

ng

/g w

w)

Mean MeHg in Soil of the South River, VA, Floodplain

Downstream River Kilometer (0 = Waynesboro Point Source)

RVP ARB NPK BPK HPK DMS RTR CRM FOR BVD GGC CNF

Wet Weight Basis (ww) ± 1 SEM

Outlier

Page 16: Survey of the Mercury Content of Earthworms on the South River Floodplain

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0

50

100

150

200

250

-5 0 5 10 15 20 25 30 35 40 45

Mea

n M

eth

yl H

g (

ng

/g w

w)

Mean MeHg in Depurated Earthworms Living on the South River, VA, Floodplain

Downstream River Kilometer (0 = Waynesboro Point Source)

RVP ARB NPK BPK HPK DMS RTR CRM FOR BVD GGC CNF

Wet Weight Basis (ww) ± 1 SEM

Page 17: Survey of the Mercury Content of Earthworms on the South River Floodplain

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Mean THg in Soil vs Concentration in Depurated Earthworms

Wet Weight Basis (ww)

R2 = 0.7193

0

500

1000

1500

2000

2500

3000

3500

0 2000 4000 6000 8000 10000 12000 14000 16000 18000 20000

Soil THg (ng/g ww)

Ear

thw

orm

TH

g (

ng

/g w

w)

Page 18: Survey of the Mercury Content of Earthworms on the South River Floodplain

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0

20

40

60

80

100

120

140

160

180

200

0 1 2 3 4 5 6 7

Soil MeHg (ng/g ww)

Ea

rth

wo

rm M

eH

g (

ng

/g w

w)

Wet Weight Basis (ww)

Mean MeHg in Soil vs Concentration in Depurated Earthworms

R2=.4201

Page 19: Survey of the Mercury Content of Earthworms on the South River Floodplain

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0

0.2

0.4

0.6

0.8

1

1.2

-5 0 5 10 15 20 25 30 35 40 45

Downstream River Kilometer (0 = Waynesboro Point Source)

RVP ARB NPK BPK HPK DMS RTR CRM FOR BVD GGC CNF

Wet Weight Basis (ww)

BAF = [earthworm] / [soil]

Bioaccumulation Factor (BAF) for Total Mercury (THg) Using Depurated Earthworm Data

Page 20: Survey of the Mercury Content of Earthworms on the South River Floodplain

20

0

10

20

30

40

50

60

70

80

-5 0 5 10 15 20 25 30 35 40 45

Downstream River Kilometer (0 = Waynesboro Point Source)

RVP ARB NPK BPK HPK DMS RTR CRM FOR BVD GGC CNF

Wet Weight Basis (ww)

Bioaccumulation Factor (BAF) for Methyl Mercury (MeHg) Using Depurated Earthworm Data

BAF = [earthworm] / [soil]

Page 21: Survey of the Mercury Content of Earthworms on the South River Floodplain

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1

10

100

1000

10000

-10 0 10 20 30 40 50

Mer

cury

(n

g/g

)

Thg (Wet Weight Basis)

Mehg (Wet Weight Basis)

Downstream River Kilometer (0 = Waynesboro Point Source)

RVP ARB NPK BPK HPK DMS RTR CRM FOR BVD GGC CNF

A Comparison of THg and MeHg Concentrations in Earthworms Living on the South River, VA, Floodplain

Wet Weight Basis (ww)

Page 22: Survey of the Mercury Content of Earthworms on the South River Floodplain

22

Cation Exchange Capacity by Location

0

2

4

6

8

10

12

14

16

RVPARB

NPKBPK

HPKDM

SRTR

CRMFO

RBVD

GGCCNF

Location

Ca

tio

n E

xc

ha

ng

e C

ap

ac

ity

(m

eq

/10

0g

)

Soil Ph By Location

0

1

2

3

4

5

6

7

8

Location

Ph

Percent of Soil Organic Matter by Location

0

1

2

3

4

5

6

RVPARB

NPKBPK

HPKDM

SRTR

CRMFOR

BVDGG

CCNF

Location

Pe

rce

nt

Org

an

ic M

att

er

Percentage of Soil composed of Sand by Location

0

10

20

30

40

50

60

70

80

90

Location

Pe

rce

nt

Sa

nd

Pa

rtic

les

Soil Characteristics

Page 23: Survey of the Mercury Content of Earthworms on the South River Floodplain

23

How much Hg is tied up in earthworms on the floodplain?

5-yr floodplain - 2094 acres = 8.5 E+6 sq m Mean earthworm fresh wt = 20.6 g / sq m

Estimated earthworm fresh wt 5-yr floodplain= 1.7 E+8 g

Mean THg in undepurated earthworms = 2447 ng/g Mean MeHg in undepurated earthworms = 66 ng/g

Total Hg in earthworms on 5-yr floodplain = 4.3 E+17 ng = 426 grams Total MeHg in earthworms on 5-yr floodplain = 1.2 E+16 ng = 11.6 grams

For the large amount of area involved, this appears to be a very small proportion of the Hg present on the floodplain.

SOURCES OF ERROR IN THIS ESTIMATE: Not all of the floodplain is suitable earthworm habitat (eg parking lots); un-weighted mean biomass and THg/MeHg may be over or under estimates of true values

Page 24: Survey of the Mercury Content of Earthworms on the South River Floodplain

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Summary

Both forms of mercury are present in the soil and earthworms of the floodplain at an elevated level.

The pattern of total mercury distribution is superficially similar to that previously observed in other organisms in the river.

The methyl mercury concentrations do not follow a discernable pattern.

Total mercury concentrations in earthworm tissues are proportional to the total mercury concentration of the soil, however this is not the case in the methyl mercury concentrations.

Page 25: Survey of the Mercury Content of Earthworms on the South River Floodplain

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Path Forward

What is the food chain position of earthworms within these ecosystems?

What is the relationship between these results and those from studying other organisms along the South River?

How do these results compare with studies of the uptake of Hg by earthworms from other terrestrial sites including sewage sludge deposits and industrial wastes.

It is of interest to pursue what causes the fluctuations in MeHg within the earthworm tissues in relation to soil MeHg content. While soil is likely a contributing factor, other variables may also play a role:

microhabitat time of sampling, earthworm species composition (affects feeding habits) endogenous vs exogenous origin of MeHg etc.

While it appears that the observed patterns of Hg content in earthworms are not unexpected, there are some questions of passing interest: