Wash. Admin. Code § 173-204-562
(1) Applicability. This section defines sediment cleanup objectives and cleanup screening levels for contaminants based on protection of the benthic community in marine and low salinity sediment. They are used to:
(2) Marine sediment - Chemical criteria. The chemical concentration criteria in Table III establish the sediment cleanup objectives and cleanup screening levels chemical criteria for marine sediment. The criteria of this section shall apply to marine sediments for toxicity to the benthic community.
(g) Where chemical criteria in Table III represent the sum of individual compounds or isomers, the following methods shall be applied:
(k) The total benzofluoranthenes criterion in Table III represents the sum of the concentrations of the "B," "J," and "K" isomers.
Table III
Marine Sediment
Sediment Cleanup Objectives and
Cleanup Screening Levels
Chemical Criteria
| Chemical Parameter | mg/kg Dry Weight(Parts perMillion (ppm)Dry Weight) | mg/kg Dry Weight(Parts perMillion (ppm)Dry Weight) |
| Sediment Cleanup Objective | CleanupScreening Level | |
| Arsenic | 57 | 93 |
| Cadmium | 5.1 | 6.7 |
| Chromium | 260 | 270 |
| Copper | 390 | 390 |
| Lead | 450 | 530 |
| Mercury | 0.41 | 0.59 |
| Silver | 6.1 | 6.1 |
| Zinc | 410 | 960 |
| ChemicalParameter | mg/kg Organic Carbon(ppm carbon) | mg/kg Organic Carbon(ppm carbon) |
| Sediment Cleanup Objective | CleanupScreening Level | |
| LPAH | 370 | 780 |
| Naphthalene | 99 | 170 |
| Acenaphthylene | 66 | 66 |
| Acenaphthene | 16 | 57 |
| Fluorene | 23 | 79 |
| Phenanthrene | 100 | 480 |
| Anthracene | 220 | 1200 |
| 2-Methylnaphthalene | 38 | 64 |
| HPAH | 960 | 5300 |
| Fluoranthene | 160 | 1200 |
| Pyrene | 1000 | 1400 |
| Benz(a)anthracene | 110 | 270 |
| Chrysene | 110 | 460 |
| Total Benzofluoranthenes | 230 | 450 |
| Benzo(a)pyrene | 99 | 210 |
| Indeno(1,2,3 c,d) Pyrene | 34 | 88 |
| Dibenzo (a,h) Anthracene | 12 | 33 |
| Benzo (g,h,i) Perylene | 31 | 78 |
| 1,2 Dichlorobenzene | 2.3 | 2.3 |
| 1,4 Dichlorobenzene | 3.1 | 9 |
| 1,2,4 Trichlorobenzene | 0.81 | 1.8 |
| Hexachlorobenzene | 0.38 | 2.3 |
| Dimethyl Phthalate | 53 | 53 |
| Diethyl Phthalate | 61 | 110 |
| Di-n-butyl Phthalate | 220 | 1700 |
| Butyl Benzyl Phthalate | 4.9 | 64 |
| Bis (2-ethylhexyl) Phthalate | 47 | 78 |
| Di-n-octyl Phthalate | 58 | 4500 |
| Dibenzofuran | 15 | 58 |
| Hexachlorobutadiene | 3.9 | 6.2 |
| N-Nitrosodiphenylamine | 11 | 11 |
| Total PCBs | 12 | 65 |
| ug/kg DryWeight(Parts perBillion (ppb)Dry Weight) | ug/kg Dry Weight(Parts perBillion (ppb)Dry Weight) | |
| Phenol | 420 | 1200 |
| 2-Methylphenol | 63 | 63 |
| 4-Methylphenol | 670 | 670 |
| 2,4 Dimethyl Phenol | 29 | 29 |
| Pentachlorophenol | 360 | 690 |
| Benzyl Alcohol | 57 | 73 |
| Benzoic Acid | 650 | 650 |
(3) Marine sediment - Biological criteria. The biological effects criteria in Table IV establish the marine sediment cleanup objectives and cleanup screening levels. The criteria of this section shall apply to marine sediments for toxicity to the benthic invertebrate community.
(b) The cleanup screening levels of this section establish a minor adverse effects level, including acute or chronic adverse effects, to the benthic community. The cleanup screening level biological criteria for a sampling station is exceeded when:
(c) The acute and chronic effects biological tests of Table V shall be used to:
(d) To designate sediment quality using biological criteria, a minimum of the following shall be included in the suite of biological tests for each sediment sample as described in Table V:
(4) Marine sediment - Other toxic, radioactive, biological, or deleterious substances criteria. "Other toxic, radioactive, biological, or deleterious substances" means substances not specified in Table III, that are in, or on, sediments. They shall be at or below levels which cause minor adverse effects in marine biological resources. The department shall determine on a case-by-case basis other criteria, methods, and procedures, such as using the biological criteria of subsection (3)(a) through (g) of this section, necessary to meet the intent of this part.
Table IV
Marine Sediment Cleanup Objectives and Cleanup Screening Levels Biological Criteria
| Biological Test/Endpoint | PerformanceStandard Control | Performance Standard Reference | Sediment CleanupObjective for eachbiological test | Cleanup Screening Level for eachbiological test |
| Amphipod | ||||
| 10-day Mortality | MC ≤ 10% | MR ≤ 25% | MT ˃ 25% Absolute and MT vs MR SD (p ≤ 0.05) | MT - MR ≥ 30%andMT vs MR SD (p ≤ 0.05) |
| Larval | ||||
| Bivalve or Echinoderm Abnormality/Mortality | NC / I ≥ 0.70 | NR/NC ≥ 0.65 | (NR - NT) /NC ˃ 0.15andNT/NC vs NR/NC SD(p ≤ 0.10) | (NR - NT) /NC ˃ 0.30andNT/NC vs NR/NC SD(p ≤ 0.10) |
| Juvenile Polychaete | ||||
| Neanthes 20-day Growth | MC < 10%andMIGC ˃ 0.72 mg/individual/day (or case-by-case) | MIGR /MIGC˃ 0.80 | MIGT /MIGR < 0.70andMIGT vs MIGR SD (p ≤ 0.05) | MIGT /MIGR < 0.50andMIGT vs MIGR SD (p ≤ 0.05) |
| Microtox | ||||
| Microtox Decreased Luminescence | case-by-case | case-by-case | MLT /MLR < 0.80andMLT vs MLR SD (p = 0.05) | |
| Benthic Abundance | ||||
| Benthic Abundance | See Table IV legend | AT/AR < 0.50For any one of three major taxaClass Crustacea, PhylumMollusca or ClassPolychaeta | AT/AR < 0.50For any two of three major taxaClass Crustacea,Phylum Mollusca orClass Polychaeta |
| Table IV Explanatory Notes: |
| A = Abundance; | |
| AFDW = Ash free dry weight; | |
| C = Control; | |
| R = Reference; | |
| T = Test; | |
| I = Initial count; | |
| M = Mortality; | |
| N = Normal survivorship expressed as actual counts; | |
| MIG = Mean individual growth rate expressed in mg/ind/day AFDW; | |
| ML = Mean light output; | |
| SD = Statistically significant difference; | |
| An exceedance of the criteria requires a statistically significant difference at p ≤ 0.05 for Amphipod, Juvenile Polychaete, Microtox tests; | |
| An exceedance of the criteria requires a statistically significant difference at p ≤ 0.10 for the Larval tests. | |
| Benthic Abundance: The reference benthic macroinvertebrate assemblage should be representative of areas removed from significant sources of contaminants and, to the extent possible, have the following characteristics: | |
| (1) The taxonomic richness of benthic macroinvertebrates and the abundances of higher taxonomic groups that reflect seasonality and natural, physical, and chemical conditions (e.g., grain size composition, salinity of sediments, water depth) in a reference area and not be obviously depressed as a result of chemical toxicity; | |
| (2) Normally abundant species that are known to be sensitive to chemical contaminants are present; | |
| (3) Normally rare species that are known to become abundant only under chemically disturbed conditions are rare or absent; and | |
| (4) The abundances of normally rare species that control benthic community structure through physical modification of the sediment are similar to those observed at the test sediment site. |
Table V
Types of Marine Sediment Biological Tests, Species, and Applicable Endpoints.
| Species/Class, biological test, and endpoint | Acuteeffectsbiological test | Chroniceffectsbiological test |
| Amphipod:Rhepoxynius abronius, Ampelisca abdita, Eohaustorius estuarius | ||
| 10-day Mortality | X | |
| Larval: Crassostrea gigas (Pacific oyster), Mytilus (edulis) galloprovincialis (Blue mussel), Strongylocentrotus purpuratus (Purple sea urchin), Dendraster excentricus (Sand dollar) | ||
| Mortality/Abnormality | X | |
| Juvenile Polychaete: | ||
| Neanthes arenaceodentata | ||
| 20-day Growth | X | |
| Microtox: Vibrio fisheri | ||
| 15-minute exposure; Decreased luminescence | X | |
| Benthic Infauna: Class Crustacea, Polychaeta, Phylum Mollusca | X |
[Statutory Authority: Chapter 70.105D RCW. WSR 13-06-014 (Order 08-07), amended and recodified as § 173-204-562, filed 2/25/13, effective 9/1/13. Statutory Authority: RCW 90.48.220. WSR 96-02-058, § 173-204-520, filed 12/29/95, effective 1/29/96. Statutory Authority: Chapters 43.21C, 70.105D, 90.48, 90.52, 90.54 and 90.70 RCW. WSR 91-08-019 (Order 90-41), § 173-204-520, filed 3/27/91, effective 4/27/91.]