draft data - do not cite or quote sediment contamination sediment toxicity benthic community...

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Draft data - do not cite or quote Sediment contamination Sediment toxicity Benthic community structure Results used to identify and map areas of unimpacted to clearly impacted sediments Current RMP toxicity tests are those recommended for the accepted statewide SQO methods for bays and estuaries, EXCEPT… Sediment Quality Assessment xicity test data used in a weight-of-evidenc

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Page 1: Draft data - do not cite or quote Sediment contamination Sediment toxicity Benthic community structure Results used to identify and map areas of unimpacted

Draft data - do not cite or quote

Sediment contamination

Sediment toxicity

Benthic community structure

Results used to identify and map areas of unimpacted to clearly impacted sediments

Current RMP toxicity tests are those recommended for the accepted statewide SQO methods for bays and estuaries, EXCEPT…

Sediment Quality Assessment

Toxicity test data used in a weight-of-evidence:

Page 2: Draft data - do not cite or quote Sediment contamination Sediment toxicity Benthic community structure Results used to identify and map areas of unimpacted

Draft data - do not cite or quote

Excerpt from SQO Staff Report - Table 5.2List of candidate sediment toxicity tests

The SQO recommends the use of sediment water interface (SWI) samples

SpeciesTaxonomic

GroupDuration

(days) Matrix Endpoint(s) CitationAmpelisca abdita Eohaustorius estuarius Rhepoxynius abronius Leptocheirus

Amphipod 10Whole

sedimentSurvival

USEPA 1994,

ASTM 1996

Mytilus galloprovincialis Mussel 2Sediment Interface

Embryo development

Anderson et al. 1996

Page 3: Draft data - do not cite or quote Sediment contamination Sediment toxicity Benthic community structure Results used to identify and map areas of unimpacted

Draft data - do not cite or quote

Mussel embryo development

48-h exposureSublethal endpoint

Sediment elutriate VS. Sediment-water interface exposure

Page 4: Draft data - do not cite or quote Sediment contamination Sediment toxicity Benthic community structure Results used to identify and map areas of unimpacted

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In April-08 the TRC decided that the

RMP S&T will adopt the

sediment-water interface (SWI)

bivalve test in 2008

using intact sediment cores.

Page 5: Draft data - do not cite or quote Sediment contamination Sediment toxicity Benthic community structure Results used to identify and map areas of unimpacted

Draft data - do not cite or quote

Issues Considered

• Comparison to historic RMP/other programs

• Interpretation (Ecological Relevance)

• Cost

Page 6: Draft data - do not cite or quote Sediment contamination Sediment toxicity Benthic community structure Results used to identify and map areas of unimpacted

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Comparison to historic RMP data

1999 - 2001 Bivalve Methods Study

• 48-hr. sublethal development test

• Elutriate (1:4 dil. VS. SWI intact cores)

• 14 stations (52 samples).

Page 7: Draft data - do not cite or quote Sediment contamination Sediment toxicity Benthic community structure Results used to identify and map areas of unimpacted

Draft data - do not cite or quote

RiversGrizzly BayNapa RiverDavis Point

Coyote Creek

San Bruno Shoal

Horseshoe Bay

Redwood Creek South Bay

 

RMP 1999-2001 Elutriate & SWI bivalve development tests (N=52)

Station Code

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08Crusie Number

% N

orm

al A

live

(Mytilus)

Elutriate

SWI (intact)

yellow = Toxic

BA10

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

BA21

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

BA41

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

BB15

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

BB70

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

BC11

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08BC21

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

BC60

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

BD41

0

20

40

60

80

100

120

1999-02 1999-07 2000-07 2001-08

BD50

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

BF21

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

BG20

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

BG30

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

Yerba Buena Is

Red Rock

Alameda

C-3-0

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

San Jose (LEMP)

Page 8: Draft data - do not cite or quote Sediment contamination Sediment toxicity Benthic community structure Results used to identify and map areas of unimpacted

Draft data - do not cite or quote

0%

50%

100%

0%

50%

100%

0%

50%

100%

Rivers

Grizzly BayNapa RiverDavis Point

0%

50%

100%

0%

50%

100%

Redwood Creek

0%

50%

100%

Yerba Buena Island

Horseshoe Bay

Coyote Creek

San Jose

0%

50%

100%

Legend:

0%

50%

100%

Sampling Period (1993 to 2001)

Amph % Survival Biv % Norm. Dev.

Amphipod and Bivalve Sediment Toxicity Results 1993-2001(BF21)

Pulse of the Estuary, 20030%

50%

100%

0%

50%

100%

0%

50%

100%

South Bay(BA21)

Page 9: Draft data - do not cite or quote Sediment contamination Sediment toxicity Benthic community structure Results used to identify and map areas of unimpacted

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Interpretation• SWI tests are thought to be more

ecologically relevant

• However, not much in known about contaminant flux and exposure

• SCCWRP study (4 samples) to determine if homogenized sediments can be left to equilibrate and used in the SWI test.

Page 10: Draft data - do not cite or quote Sediment contamination Sediment toxicity Benthic community structure Results used to identify and map areas of unimpacted

Draft data - do not cite or quote

Current Status• RMP S&T 2008 will switch to collecting

intact cores for the SWI bivalve development test to be comparable to recommended SQO methods that have been endorsed by a panel of national experts

This will result in a NEW toxicity measure and will not be comparable with historic RMP data (largely an issue in Suisun Bay & Lower South Bay Regions)

Page 11: Draft data - do not cite or quote Sediment contamination Sediment toxicity Benthic community structure Results used to identify and map areas of unimpacted

Draft data - do not cite or quote

Question for EEPSShould the RMP continue the bivalve elutriate

tests in Suisun Bay and Lower South Bay Regions?

+ evaluate chemistry in the overlying water of both tests to begin to understand differences in contaminant exposure between intact cores and homogenized sediment elutriates

Page 12: Draft data - do not cite or quote Sediment contamination Sediment toxicity Benthic community structure Results used to identify and map areas of unimpacted

Draft data - do not cite or quote

RiversGrizzly BayNapa RiverDavis Point

Coyote Creek

San Bruno Shoal

Horseshoe Bay

Redwood Creek South Bay

 

RMP 1999-2001 Elutriate & SWI bivalve development tests (N=52)

Station Code

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08Crusie Number

% N

orm

al A

live

(Mytilus)

Elutriate

SWI (intact)

yellow = Toxic

BA10

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

BA21

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

BA41

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

BB15

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

BB70

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

BC11

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08BC21

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

BC60

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

BD41

0

20

40

60

80

100

120

1999-02 1999-07 2000-07 2001-08

BD50

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

BF21

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

BG20

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

BG30

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

Yerba Buena Is

Red Rock

Alameda

C-3-0

0

20

40

60

80

100

1999-02 1999-07 2000-07 2001-08

San Jose (LEMP)

Page 13: Draft data - do not cite or quote Sediment contamination Sediment toxicity Benthic community structure Results used to identify and map areas of unimpacted

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CostCost

EstimateAdditional

Cost Description

Current Tests: $39,814 - Amphipod & Bivalve Elutriate test @ 27 stations

Adopt SWI tests: $40,360 $545 Amphipod & Bivalve SWI test @ 27 stations

Adopt SWI tests & add Elutriate

test at SB & LSB stations:

$46,824 $7,009 Amphipod & Bivalve SWI test @ 27 stations Plus Bivalve Elutriate test at 10 stations

Page 14: Draft data - do not cite or quote Sediment contamination Sediment toxicity Benthic community structure Results used to identify and map areas of unimpacted

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Cost

Toxicity TestCost per Sample Total Samples

Total for Task

(incl. OH)

Amphipod Eohaustorius Toxicity Test $820 27 $22,361with Solid-Phase Sediment

Bivalve Embryo/Larval Toxicity Test $640 27 $17,453with Sediment Elutriates

Bivalve Embryo/Larval Toxicity Test $660 27 $17,998at the Sediment-Water Interface (SWI)

Sampling costs will not increase beyond budget

$20 more per sample