Office of Water 

Office Science and 

Technology 

EPA 820-D-14-005 

May 2014 

Draft Update of Human Health
 

Ambient Water Quality Criteria:
 

Aldrin
 

309-00-2
 
 

 

 

 

 

 

EPA 820-D-14-005 

May 2014 

Update of Human Health
 

Ambient Water Quality Criteria:
 

Aldrin
 

309-00-2
 

Draft 

Office of Science and Technology
 

Office of Water
 

U.S. Environmental Protection Agency
 

Washington, DC 20460
 
 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

Aldrin 309-00-2 

Table of Contents 

Introduction: Plan and Scope of Update 

Problem Formulation 

Criteria Formulas- Analysis Plan 

Exposure Factors 

Body Weight 

Drinking Water Intake 

Fish Consumption Rate 

Bioaccumulation Factor 

Hazard Identification and Dose Response: Cancer Slope Factor 

Criteria Derivation- Analysis 

Criteria Characterization 

Chemical Name / Synonyms 

References 

Introduction: Plan and Scope of Update 

Human health ambient water quality criteria (AWQC) are numeric values for pollutant 

concentrations in ambient waters that the U.S. Environmental Protection Agency (EPA) 

considers to be protective of human health. EPA periodically revises water quality criteria to 

ensure that they reflect the latest scientific knowledge. The current revisions of the criteria for 

aldrin *

, contained in this document, incorporate updated information regarding body weight, 

drinking water intake, fish consumption rate, and bioaccumulation. Updated body weight and 

͇ιΊΣΙΊΣͽ Ϯ̯χ͋ι ΊΣχ̯Ι͋ ͇̯χ̯ ̯ι͋ Ί͇͋ΣχΊ͕Ί͇͋ ΊΣ E ́!͛ν ·EϳζΪνϢι͋ F̯̽χΪιν H̯Σ͇̼ΪΪΙ ́ 2011 E͇ΊχΊΪΣ͛ 

(USEPA, 2011). The bioaccumulation factor data Ίν Ϣζ͇̯χ͇͋ ϢνΊΣͽ E ́!͛ν Estimation Program 

Interface (EPI) Suite modeling program (USEPA, 2012a). The overall fish consumption rate and 

trophic level breakdowns are updated using E ́!͛ν ·EνχΊ΢̯χ͇͋ FΊν· ΪΣνϢ΢ζχΊΪΣ ·̯χ͋ν ͕Ϊι χ·͋ 

U.S. Population and Selected Subpopulations (NHANES 2003-2010)͛ (Ε΋E ́!΂ 2014). Unless 

otherwise specified, all sources of information used in this update are from peer reviewed 

sources. 

Note that the term "water quality criteria" can carry one of two possible meanings, 

depending on the section of the Clean Water Act (CWA) associated with the particular criteria 

̯χ ΊννϢ͋ ̈́ ͞Ρ̯χ͋ι θϢ̯ΜΊχΘ ̽ιΊχ͋ιΊ̯͟ ΢̯Θ ι͕͋͋ι χΪ Σ̯χΊΪΣ̯Μ Ϯ̯χ͋ι θϢ̯ΜΊχΘ ̽ιΊχ͋ιΊ̯ ι͋̽Ϊ΢΢͋Σ͇̯χΊΪΣν 

issued under CWA § 304 ̈́ ͞Ρ̯χ͋ι θϢ̯ΜΊχΘ ̽ιΊχ͋ιΊ̯͟ ΢̯Θ ̯ΜνΪ ι͕͋͋ι χΪ Ϯ̯χ͋ι θϢ̯ΜΊχΘ ̽ιΊχ͋ιΊ̯ 

components of water quality standards adopted by states, territories, or authorized tribes 

under CWA § 303. 

National ambient water quality criteria recommendations for human health are issued 

by the EPA under CWA §304. They are based on the latest scientific information on the 

relationship between the effects of a constituent concentration and human health. Protective 

* This compound is not currently registered as a pesticide by EPA. 

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assumptions are made regarding the potential human exposure intakes. These criteria do not 

reflect consideration of non-human health endpoints or economic impacts. Nor do they reflect 

the technological feasibility of meeting the chemical concentrations in ambient water. National 

ambient water quality criteria recommendations for human health are not automatically 

incorporated into water quality standards adopted by states, territories, or authorized tribes. 

Rather, they provide scientific information to states, territories and authorized tribes to assist 

them in adopting ambient water quality criteria for human health in water quality standards 

that meet CWA requirements. National ambient water quality criteria recommendations for 

human health are not regulations themselves and they do not impose legally binding 

requirements on EPA, states, territories, authorized tribes, or the public. States, territories, and 

authorized tribes have the discretion to adopt, where appropriate, other scientifically 

͇͕͋͋ΣνΊ̼Μ͋ Ϯ̯χ͋ι θϢ̯ΜΊχΘ ̽ιΊχ͋ιΊ̯ χ·̯χ ͇Ί͕͕͋ι ͕ιΪ΢ E ́!͛ν Σ̯χΊΪΣ̯Μ ̯΢̼Ί͋Σχ ι͋̽Ϊ΢΢͋Σ͇͇͋ ̽ιΊχ͋ιΊ̯ 

for human health. 

Ambient water quality criteria components of water quality standards are generally 

adopted by the states, territories, and authorized tribes themselves, under §303(c)(2). (In 

certain circumstances EPA also may promulgate this type of criterion itself, pursuant to 

§303(c)(4)). State ambient water quality criteria for human health represent a quality of water 

that sufficiently protects human health to support a designated use of the state, territory, or 

authorized tribe. Such criteria may be expressed in terms of constituent concentrations, levels, 

or narrative statements. Once ambient water quality criteria for human health are adopted by a 

state, territory, or authorized tribe into their water quality standards, they provide a basis for 

controlling discharges or releases of pollutants, for developing permit limits, assessing waters, 

and developing total maximum daily loads (TMDLs) for waters that do not meet the water 

quality standard. Ambient water quality criteria for human health have a regulatory impact 

once they have been adopted into water quality standards by the state, territory, or authorized 

tribe under § 303(c)(2) (or alternatively issued by EPA pursuant to § 303(c)(4)). 

The water quality criteria at issue in this document are national ambient water quality 

criteria recommendations for human health issued under CWA § 304. Unless expressly 

ΊΣ͇Ί̯̽χ͇͋ Ϊχ·͋ιϮΊν͋΂ ̯ΜΜ ι͕͋͋ι͋Σ̽͋ν χΪ ̽͞ιΊχ͋ιΊ̯΂͟ ͞Ϯ̯χ͋ι θϢ̯ΜΊχΘ ̽ιΊχ͋ιΊ̯΂͟ ̯͞΢̼Ί͋Σχ Ϯ̯χ͋ι θϢ̯ΜΊχΘ 

̽ιΊχ͋ιΊ̯ (!ΡΆ) ι͋̽Ϊ΢΢͋Σ͇̯χΊΪΣν΂͟ Ϊι νΊ΢ΊΜ̯ι ϭ̯ιΊ̯Σχν χ·͋ι͋Ϊ͕΂ ̯ι͋ ι͕͋͋ι͋Σ̽͋ν χΪ Σ̯χΊΪΣ̯Μ 

ambient water quality criteria recommendations for human health. 

Problem Formulation 

Problem formulation provides a strategic framework for water quality criteria 

development by focusing on the most relevant endpoints and increasing the transparency of 

the effects assessment process. The structure of this criteria document is consistent with U.S. 

E ́!͛ν ·Framework for Human Health Risk Assessment to Inform Decision Making͛ (USEPA, 

2012b). 

In the development of AWQC, EPA currently follows the deterministic assessment 

methodology outlined in E ́!͛ν ·Methodology for Deriving Ambient Water Quality Criteria for 

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the Protection of Human Health (2000)͛ (USEPA, 2000), hereafter known as the 2000 

Methodology. For the development of criteria for carcinogens that express a non-threshold, 

linear dose response, the 2000 Methodology takes into consideration exposure factors (body 

weight, drinking water intake, fish consumption, and bioaccumulation), the increased cancer 

risk due to exposure to the pollutant, and a 10-6 (or 1 in 1,000,000) risk level for the general 

population. The 10-6 risk level utilized in the derivation of the AWQC represents the water 

̽ΪΣ̽͋Σχι̯χΊΪΣ χ·̯χ ϮΪϢΜ͇ ̼͋ ͋ϳζ͋̽χ͇͋ χΪ ΊΣ̽ι̯͋ν͋ ̯Σ ΊΣ͇ΊϭΊ͇Ϣ̯Μ͛ν ΜΊ͕͋χΊ΢͋ cancer risk from 

exposure to the particular pollutant by no more than one chance in one million, regardless of 

the additional lifetime cancer risk due to exposure, if any, to that particular substance from 

other sources. States and authorized tribes may consider adjusting exposure assumptions and 

related model inputs according to guidance in the 2000 Methodology, to assure that 

subpopulations are adequately protected if data are available. 

Criteria Formulas- Analysis Plan 

The following formulas are used to develop E ́!͛ν Ρ! ΋͋̽χΊon 304(a) human health 

ambient water quality criteria. EPA develops criteria for ambient waters typically considering 

two routes of exposure. The first formula can be used to derive a human health criterion that 

assumes exposure through both the consumption of water and the consumption of aquatic 

organisms. The second formula can be used to derive a criterion that assumes exposure 

through the consumption of aquatic organisms, but not water. The use of one criterion over the 

other depends on the designated use of the water bodies in question (i.e. drinking water source 

and/or fishable waters). 

EPA recommends inclusion of the drinking water exposure pathway for ambient surface 

waters where drinking water is a designated use for the following reasons: (1) Drinking water is 

a designated use for surface waters under the CWA, and therefore, criteria are needed to 

assure that this designated use can be protected and maintained. (2) Although rare, there are 

some public water supplies that provide drinking water from surface water sources without 

treatment. (3) Even among the majority of water supplies that do treat surface waters, existing 

treatments may not necessarily be effective for reducing levels of particular contaminants. (4) 

͜Σ ̽ΪΣνΊ͇͋ι̯χΊΪΣ Ϊ͕ χ·͋ !ͽ͋Σ̽Θ͛ν goals of pollution prevention, ambient waters should not be 

contaminated to a level where the burden of achieving health objectives is shifted away from 

those responsible for pollutant discharges and placed on downstream users to bear the costs of 

upgraded or supplemental water treatment (USEPA, 2000). 

EPA recommends the organism only criterion in those cases where the designated uses 

of a water body include only supporting fishable uses under Section 101(a) of the CWA, and 

thus, fish or shellfish for human consumption, but not as a drinking water supply source (e.g., 

non-potable estuarine waters) (USEPA, 2000). 

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Where: 

AWQC = ambient water quality criteria (at the 10-6 risk level) 

CSF = cancer slope factor 

BW = body weight 

DI = drinking water intake 

∑ 4 νϢ΢΢̯χΊΪΣ Ϊ͕ ϭ̯ΜϢ͋ν ͕Ϊι ̯θϢ̯χΊ̽ χιΪζ·Ί̽ Μ͋ϭ͋Μν (Αͫ) Ϯ·͋ι͋ χ·͋ Μ͋χχ͋ι ͞Ί͟ νχ̯Σ͇ν ͕Ϊι χ·͋ i=2 

trophic levels to be considered, starting with TL 2 and proceeding to TL 4 

FCRi = fish consumption rate for aquatic trophic levels 2, 3, and 4 

BAFi = bioaccumulation factor for aquatic trophic levels 2, 3, and 4 

 

 

 

† 10-6 or 1 in 1,000,000 risk level for the general population 

‡ 1000 μg/mg is used to convert the units of mass into micrograms from milligrams. 

Aldrin 309-00-2 

The formulas for deriving the criteria values are as follows (USEPA, 2000): 

For consumption of water and organisms: 

 (Eq. 1) 

 

AWQC (μg/L) = [10-6† / CSF (kg·d/mg)] × BW (kg) × 1000 (μg/mg)‡ 

4 DI (L/d) + ∑ (F·Ί (Ιͽ /͇) ∓ !FΊ (ͫ Ιͽ)) Ί 2 

For consumption of organisms only: 

 (Eq. 2) 

 

AWQC (μg/L) = [10-6† / CSF (kg·d/mg)] × BW (kg) × 1000 (μg/mg)‡

∑4 (F·Ί (Ιͽ/ ͇) ∓ !FΊ (ͫ Ιͽ)) Ί 2 

The following sections identify each of the components of the formulas for the human 

health ambient water quality criteria and provide reference sources, previously used values 

when available, and the values to be used in the updated criteria. 

Exposure Factors: 

Body Weight 

The updated recommended body weight (BW) is 80 kg which represents the mean 

weight for adults 21 years of age and older. Α·Ίν ι͋̽Ϊ΢΢͋Σ͇̯χΊΪΣ Ίν ͕ΪϢΣ͇ ΊΣ E ́!͛ν ·Exposure 

F̯̽χΪιν H̯Σ͇̼ΪΪΙ ́ 2011 E͇ΊχΊΪΣ͛ in Chapter 8. It was based on data derived from the National 

Health and Nutrition Examination Survey (NHANES) 1999−2006 (USEPA, 2011). This body 

weight replaces the recommended standard weight for adults of 70 kg that was described in 

the 2000 Methodology which was approximated from the mean body weight of adults from the 

National Health and Nutrition Examination Survey (NHANES) III database (1988-1994) and a 

1989 study by the National Cancer Institute (USEPA, 2000). 

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Drinking Water Intake 

The updated drinking water intake (DI) is 3 L/day, rounded from 3.091 L/day for 

consumer-only estimates of direct and indirect water ingestion based on NHANES 2003-2006 

data for all sources of water at the 90th ζ͋ι̽͋ΣχΊΜ͋ ͕Ϊι ̯͇ϢΜχν (≥21 Θ̯͋ιν of age) (USEPA, 2011). 

Direct water is defined as water ingested directly as a beverage (from all sources); indirect 

water is defined as water added in the preparation of food or beverages, not including indirect 

consumption of bottled water. This recommended value Ίν ͕ΪϢΣ͇ ΊΣ E ́!͛ν ·Exposure Factors 

H̯Σ͇̼ΪΪΙ ́ 2011 E͇ΊχΊΪΣ͛ in Table 3-36. It replaces the drinking water intake standard of 2 L/day 

described in the 2000 Methodology which represented the 86th percentile for adults 20 years 

̯Σ͇ ΪΜ͇͋ι ΊΣ χ·͋ Ε΋ D͋ζ̯ιχ΢͋Σχ Ϊ͕ !ͽιΊ̽ϢΜχϢι͋͛ν 1994-96 Continuing Survey of Food Intake by 

Individuals (CSFII) analysis or the 88th percentile of adults in the National Cancer Institute study 

of the 1977-78 Nationwide Food Consumption Survey (USEPA, 2000). 

Fish Consumption Rate 

The updated fish consumption rate (FCR) for the general adult population is 22 

grams/day (0.022 kg/day) (USEPA, 2014: see Table 9a). It represents the 90th percentile per 

capita consumption rate of freshwater and estuarine fish for the U.S. adult population 21 years 

of age and older based on the Centers for Disease Control and Prevention (CDC) National 

Health and Nutrition Examination Surveys (NHANES) conducted from 2003-2010. It replaces the 

FCR default of 17.5 grams/day, which represented an estimate of the 90th percentile per capita 

consumption rate of freshwater and estuarine fish for the U.S. adult population based on the 

Ε ̈́΋ ̈́ D͋ζ̯ιχ΢͋Σχ Ϊ͕ !ͽιΊ̽ϢΜχϢι͋͛ν (Ε΋D!͛ν) ΪΣχΊΣϢΊΣͽ ΋Ϣιϭ͋Θ Ϊ͕ FΪΪ͇ ͜Σχ̯Ι͋ ̼Θ ͜Σ͇ΊϭΊ͇Ϣ̯Μν 

(CSFII) 1994-96 data (USEPA, 2002a). 

As recommended in the 2000 Methodology, this update to the criteria distinguishes a 

trophic level (TL) breakdown of the fish consumption rate to provide a better representation of 

͇Ί͋χ̯ιΘ ͋ϳζΪνϢι͋ χΪ ͕Ίν· ̯χ ΢ϢΜχΊζΜ͋ χιΪζ·Ί̽ Μ͋ϭ͋Μν ̈́ !Σ Ϊιͽ̯ΣΊν΢͛ν χιΪζ·Ί̽ ζosition in the aquatic 

food web can have an important effect on the magnitude of bioaccumulation of certain 

chemicals. The trophic levels are numbered 2, 3, and 4 and account for different categories of 

fish and shellfish species based on their position in the aquatic food web. TL2 accounts for 

benthic filter feeders, TL3 accounts for forage fish, and TL4 accounts for predatory fish. 

In order to derive the trophic level breakdown of the 22 grams/day freshwater and 

estuarine FCR, the trophic level specific freshwater and estuarine FCR data sets for adults 21 

years of age and older were identified (USEPA, 2014: see Tables 16a, 17a, and 18a). In each 

χιΪζ·Ί̽ Μ͋ϭ͋Μ νζ͋̽Ί͕Ί̽ ͇̯χ̯ ν͋χ΂ χ·͋ ι̯χΊΪ Ϊ͕ χ·̯χ χιΪζ·Ί̽ Μ͋ϭ͋Μ͛ν 90th percentile FCR compared to 

the summation of all three trophic level specific 90th percentile FCRs was applied to the 22 

grams/day FCR used in this update. The trophic level ratios were calculated as follows: TL ratio 

= 90th percentile FCR for the TL divided by the sum of the 90th percentile FCRs for all TLs. TL2 = 

7.6/21.3 = 0.3568 (35.68%), TL3 = 8.6/21.3 = 0.4038 (40.38%), and TL4 = 5.1/21.3 = 0.2394 

(23.94%). Applying these ratios to the updated FCR of 22 grams/day result in trophic level 

breakdowns of TL2 = 8 grams/day (0.008 kg/day); TL3 = 9 grams/day (0.009 kg/day); and TL4 = 5 

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Aldrin 309-00-2 

grams/day (0.005 kg/day). These resulting trophic level FCRs are well within the confidence 

ΊΣχ͋ιϭ̯Μν ͕Ϊι ̯͋̽· Ϊ͕ χ·͋ χιΪζ·Ί̽ Μ͋ϭ͋Μ νζ͋̽Ί͕Ί̽ ͇ΊνχιΊ̼ϢχΊΪΣν͛ 90th percentiles and add to the total 

of 22 grams/day (USEPA, 2014). 

Bioaccumulation Factor 

Several attributes of the bioaccumulation process are important to understand when 

deriving national BAFs for use in setting national 304(a) criteria. First, the term 

̼͞ΊΪ̯̽̽Ϣ΢ϢΜ̯χΊΪΣ͟ ι͕͋͋ιν χΪ χ·͋ Ϣζχ̯Ι͋ ̯Σ͇ ι͋χ͋ΣχΊΪΣ of a chemical by an aquatic organism 

from ̯ΜΜ νϢιιΪϢΣ͇ΊΣͽ ΢͇͋Ί̯ (͋ ̈́ͽ ̈́΂ Ϯ̯χ͋ι΂ ͕ΪΪ͇΂ ν͇͋Ί΢͋Σχ) ̈́ Α·͋ χ͋ι΢ ̼͞ΊΪ̽ΪΣ̽͋Σχι̯χΊΪΣ͟ ι͕͋͋ιν χΪ 

the uptake and retention of a chemical by an aquatic organism from water only. For some 

chemicals (particularly those that are highly persistent and hydrophobic), the magnitude of 

bioaccumulation by aquatic organisms can be substantially greater than the magnitude of 

bioconcentration. Thus, an assessment of bioconcentration alone may underestimate the 

extent of accumulation in ̯θϢ̯χΊ̽ ̼ΊΪχ̯ ͕Ϊι χ·͋ν͋ ̽·͋΢Ί̯̽Μν ̈́ !̽̽Ϊι͇ΊΣͽΜΘ΂ E ́!͛ν ͽϢΊ͇͋ΜΊΣ͋ν 

presented in the 2000 Methodology emphasize the measurement or estimation of chemical 

bioaccumulation by aquatic organisms (USEPA, 2000). 

The bioaccumulation factors (BAF) have been estimat͇͋ ϢνΊΣͽ E ́!͛ν EνχΊ΢̯χΊΪΣ  ́ιΪͽι̯΢ 

͜Σχ͋ι͕̯̽͋ (E ́͜) ΋ϢΊχ͋ (Ε΋E ́!΂ 2012̯) ̈́ Α·͋ F!FTM ζιΪͽι̯΢ ϮΊχ·ΊΣ E ́͜ ΋ϢΊχ͋ estimates fish 

bioaccumulation factors using octanol-water partition coefficients (KOW) and biotransformation 

data from a model designed by Arnot and Gobas (2003). The model includes mechanistic 

processes for bioaccumulation such as chemical uptake from the water at the gill surface and 

from the diet, chemical elimination at the gill surface, fecal egestion, growth dilution and 

metabolic biotransformation. Other processes included in the calculations are bioavailability in 

the water column (only the freely dissolved fraction can bioconcentrate) and absorption 

efficiencies at the gill and in the gastrointestinal tract. The model requires the octanol-water 

partition coefficient (KOW) of the chemical and the normalized whole-body metabolic 

biotransformation rate constant as input parameters to predict BAF values. Model predictions 

may be highly uncertain for chemicals that have estimated log KOW values > 9. The model is not 

recommended at this time for chemicals that appreciably ionize, for pigments and dyes, or for 

perfluorinated substances (USEPA, 2012a). 

For aldrin, BAFs have been estimated using the EPI Suite model (USEPA, 2012a) as 

described above for trophic levels 2, 3, and 4. The estimated lower (TL2), mid (TL3), and upper 

(TL4) trophic level BAFs for aldrin (log KOW = 6.50) are 222,600 L/kg, 207,700 L/kg, and 184,000 

L/kg wet-weight, respectively. These estimated BAFs replace the bioconcentration factor (BCF) 

of 4,670 L/kg used in the 2002 criteria derivations, which was calculated for dieldrin from 

bioconcentration studies and used for aldrin due to rapid conversion of aldrin to dieldrin by 

aquatic organisms and represented all trophic levels (USEPA, 1980). 

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Aldrin 309-00-2 

Hazard Identification and Dose Response: Cancer Slope Factor 

Aldrin is characterized as a class B2 probable human carcinogen following the 1986 EPA 

Guidelines for Carcinogen Risk Assessment (USEPA, 1986; USEPA, 1993). 

The cancer slope factor (CSF) is an upper bound, approximating a 95% confidence limit, 

on the increased cancer risk from a lifetime oral exposure to an agent. The CSF for aldrin is 17 

per mg/kg·day (USEPA, 1993). 

The principle studies by Davis (1965) and National Cancer Institute (NCI, 1978) chosen to 

calculate the cancer slope factor for aldrin were based on development of liver carcinomas in 

mice orally exposed to aldrin (USEPA, 1993). 

Criteria Derivation- Analysis 

Table 1 summarizes model inputs used to derive the 2014 updated human health 

ambient water quality criteria for aldrin. Criteria calculations are presented below. These 

updated aldrin criteria recommendations are based on the 2000 Methodology and updated 

exposure assumptions as described above (Exposure Factors). 

Table 1. Summary of input parameters for 2014 human health ambient water quality criteria 

for aldrin 

Component Value Source Input Characterization 

CSF 17 per mg/kg·day USEPA, 

1993 

an upper bound, approximating a 95% confidence 

limit, on the increased cancer risk from a lifetime 

exposure to an agent by ingestion 

BW 80 kg USEPA, 

2011 mean weight for adults (≥21 Θ̯͋ιν Ϊ͕ ̯ͽ͋) 

DI 3 L/day USEPA, 

2011 90th ζ͋ι̽͋ΣχΊΜ͋ ͕Ϊι ̯͇ϢΜχν (≥21 Θ̯͋ιν of age) 

FCR 

TL2 0.008 kg/day USEPA, 

2014 

90th percentile consumption rate for the U.S. adult 

ζΪζϢΜ̯χΊΪΣ (≥21 Θ̯͋ιν Ϊ͕ ̯ͽ͋) TL3 0.009 kg/day 

TL4 0.005 kg/day 

BAF 

TL2 222,600 L/kg 

USEPA, 

2012a 

EPI Suite KOW model estimated steady-state BAF 

values for non-ionic organic chemicals in 3 general 

trophic levels of fish in temperate environments 

(10°C) 

TL3 207,700 L/kg 

TL4 184,000 L/kg 

For consumption of water and organisms:
 

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 ==

AWQC (μg/L) = [10-6 / CSF (kg·d/mg)] × BW (kg) × 1000 (μg/mg)
 4 DI (L/d) + ∑ (F·Ί (Ιͽ ͇) ∓ !FΊ (ͫ /Ιͽ)) Ί=2
 

 

 

 

= 10-6 / 17 kg·d/mg × 80 kg × 1000 μg/mg 

3 L/d + ((0.008 kg/d × 222,600 L/kg) + (0.009 kg/d × 207,700 L/kg) + (0.005 kg/d × 184,000 L/kg)) 

= 0.00000103 μg/L (rounded to 0.0000010 μg/L because of significant figures, see 2000 Methodology) 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

Aldrin 309-00-2 

For consumption of organisms only: 

 

 

 

 

 

AWQC (μg/L) = [10-6 / CSF (kg·d/mg)] × BW (kg) × 1000 (μg/mg) 

∑4 (F·Ί (Ιͽ/͇) ∓ !FΊ (ͫ/ Ιͽ)) Ί=2

= 10-6 / 17 kg·d/mg × 80 kg × 1000 μg/mg 

(0.008 kg/d × 222,600 L/kg) + (0.009 kg/d × 207,700 L/kg) + (0.005 kg/d × 184,000 L/kg) 

= 0.00000103 μg/L (rounded to 0.0000010 μg/L because of significant figures, see 2000 Methodology) 

The updated magnitude of the human health ambient water quality criteria for aldrin at 

the 10-6 risk level are 0.0000010 μg/L (water and organism) and 0.0000010 μg/L (organism 

only) (Table 2). These updated criteria replace the previously published values (USEPA, 2002b). 

Table 2. ΋Ϣ΢΢̯ιΘ Ϊ͕ E ́!͛ν ζι͋̽ΊΪϢνΜΘ ι͋̽Ϊ΢΢͋Σ͇͇͋ (2002) and updated (2014) human health 

ambient water quality criteria for aldrin 

2002 Human Health AWQC 2014 Human Health AWQC 

Water and Organism 0.000049 μg/L 0.0000010 μg/L (1.0×10 -6 μg/L) 

Organism Only 0.000050 μg/L 0.0000010 μg/L (1.0×10 -6 μg/L) 

These AWQC are meant to be protective of human health for the general adult 

population from an increased cancer risk due to exposure to aldrin at a 10-6 or 1 in 1,000,000 

risk level. The 10-6 risk level associated with the AWQC represents the concentration that would 

̼͋ ͋ϳζ͋̽χ͇͋ χΪ ΊΣ̽ι̯͋ν͋ ̯Σ ΊΣ͇ΊϭΊ͇Ϣ̯Μ͛ν ΜΊ͕͋χΊ΢͋ cancer risk from exposure to the particular 

pollutant by no more than one chance in one million, regardless of the additional lifetime 

cancer risk due to exposure, if any, to that particular substance from other sources. 

Criteria Characterization 

The updated 2014 human health AWQC for aldrin take into account current data on 

health effects and exposure input parameters, consistent with the 2000 Methodology. The 

updated 2014 human health AWQC for aldrin are about an order of magnitude lower than 

E ́!͛ν ζι͋ϭΊΪϢνΜΘ ι͋̽Ϊ΢΢͋Σ͇͇͋ 2002 criteria; i.e. the water-and-organism criterion decreased 

from 0.000049 to 0.0000010 μg/L and the organism-only criterion decreased from 0.000050 to 

0.0000010 μg/L (Table 2). The following paragraphs describe the individual influence of each of 

the revised model inputs and exposure assumptions on the overall change in value. 

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Aldrin 309-00-2 

Body Weight 

E ́!͛ν Ϣζ͇̯χ͇͋ !ΡΆ ̯ννϢ΢͋ ̯ ·Ίͽ·͋ι body weight compared to the previously 

recommended 2002 criteria, reflecting a recent rise in average adult body weight among the 

U.S. population. The updated body weight assumption of 80 kg based on recent survey data 

from the 1999−2006 NHANES data is 10 kg greater than the previous recommendation of 70 kg. 

Assuming all other input parameters remain constant, a higher average body weight in the 

AWQC calculations (Eq. 1 and 2 above) results in higher AWQC. That is, as body weight 

increases, the level of a contaminant in water at or below which negative health effects are not 

anticipated from a lifetime of exposure also increases. 

Drinking Water Intake 

The updated drinking water intake assumption is 3 L/day, which is higher than the 

previously recommended rate of 2 L/day. Assuming all other input parameters remain constant, 

a higher drinking water intake assumption in the AWQC calculations (Eq. 1 and 2 above) results 

in lower AWQC. That is, as drinking water intake increases, and thus overall exposure increases, 

the level of a contaminant in water at or below which negative health effects are not 

anticipated from a lifetime of exposure decreases. 

Fish Consumption Rate 

The updated fish consumption rate is 22 g/day, divided into trophic level rates of 8 

g/day, 9 g/day, and 5 g/day for trophic levels 2, 3, and 4, respectively, which is higher than the 

previously recommended rate of 17.5 g/day. Assuming all other input parameters remain 

constant, a higher fish consumption rate assumption in the AWQC calculations (Eq. 1 and 2 

above) results in lower AWQC. That is, as fish consumption increase, and thus overall exposure 

increases, the level of a contaminant in water at or below which negative health effects are not 

anticipated from a lifetime of exposure decreases. 

Bioaccumulation Factor 

The updated AWQC rely on EPI Suite model-estimated BAFs rather than the previously 

recommended BCF of 4,670 L/kg. The lower (TL2), mid (TL3), and upper (TL4) trophic level BAFs 

assumed in the updated criteria equations (Eq. 1 and 2 above) are 222,600, 207,700, and 

184,000 L/kg wet-weight, respectively. Assuming all other input parameters remain constant, 

the higher ratios of fish tissue concentrations to water concentrations of aldrin by aquatic 

organisms result in lower AWQC. That is, as bioaccumulation or bioconcentration of a 

contaminant in fish and shellfish increases, and thus overall exposure increases, the level of a 

contaminant in water at or below which negative health effects are not anticipated from a 

lifetime of exposure decreases. The utilization of a bioaccumulation factor rather than a 

bioconcentration factor better represents the amount of a contaminant accumulating in an 

organism because it accounts not ΪΣΜΘ ͕Ϊι χ·͋ Ϊιͽ̯ΣΊν΢͛ν ͋ϳζΪνϢι͋ χΪ χ·͋ ζΪΜΜϢχ̯Σχ ΊΣ χ·͋ Ϯ̯χ͋ι 

column, but also from the food chain and surrounding environment as well as 

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Aldrin 309-00-2 

biotransformation of the pollutant in the organism due to metabolic processes. The utilization 

of the three trophic levels of fish and shellfish consumed, as opposed to representing all trophic 

levels of fish and shellfish consumed by a single value, allows for better exposure 

representation, especially when pollutants bioaccumulate in significantly different amounts for 

organisms in different trophic levels at different positions in the food chain. 

Additional routes of exposure to a particular pollutant besides exposure from water 

intake and fish consumption are possible and may be considered when setting criteria for a 

state or tribe. Possible additional routes include, but are not limited to, dermal exposure, 

inhalation exposure, marine fish and shellfish consumption (when not included in the fish 

consumption rate), and non-fish dietary exposures (fruits, vegetables, grains, meats or poultry). 

If scientific evidence exists which indicate that one or more of these routes pose a significant 

risk of exposure, states and authorized tribes are encouraged to ensure that subpopulations are 

adequately protected. 

States, territories, and authorized tribes have the flexibility to develop criteria, on a sitespecific basis, that provide additional protection appropriate for highly exposed populations. 

EPA is aware that exposure patterns in general, and fish consumption in particular, vary 

substantially. EPA understands that highly exposed populations may be widely distributed 

geographically throughout a given state, territory, or authorized tribal area. EPA recommends 

that priority be given to identifying and adequately protecting the most highly exposed 

populations. Thus, if a state, territory, or authorized tribe determines that a highly exposed 

population is at greater risk and would not be adequately protected by criteria based on the 

general population, and by the national 304(a) criteria in particular, the state, territory, or 

authorized tribe may adopt more stringent criteria using alternative exposure assumptions 

(USEPA, 2000). Subpopulations that may be considered include, but are not limited to, 

recreational fishers, subsistence fishers, women of childbearing age, and children. When 

scientific data exist showing one of these subpopulations is at risk of greater exposure to the 

pollutant or are biologically more sensitive, then the relevant inputs should be considered in 

setting criteria. This could entail raising the fish consumption rate to a level more reflective of 

the subpopulation based on collected data or adjusting the body weight and drinking water 

intake. 

Chemical Name / Synonyms 

 Aldrin (CAS Number 309-00-2)

 Aldrex

 Aldrite

 Aldrosol

 

 

1,4:5,8-Dimethanonaphthalene, 1,2,3,4,10,10-Hexachloro-1,4,4a,5,8,8a-Hexahydro-, (1

alpha, 4 alpha, 4a beta, 5 alpha, 8 alpha, 8a beta)- 

 1,4:5,8-Dimethanonaphthalene, 1,2,3,4,10,10-Hexachloro-1,4,4a,5,8,8a-Hexahydro­

 Drinox 

10
 
 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

Aldrin 309-00-2 

 ENT 15,949 

 1,2,3,4,10,10-Hexachloro-1,4,4a,5,8,8a-Hexahydro-1,4,5,8-Dimethanonaphthalene 

 1,2,3,4,10,10-Hexachloro-1,4,4a,5,8,8a-Hexahydro-1,4-endo-exo-5,8

Dimethanonaphthalene 

­

 1,2,3,4,10,10-Hexachloro-1,4,4a,5,8,8a-Hexahydro-exo-1,4-endo-5,8

Dimethanonaphthalene 

­

 Hexachlorohexahydro-endo-exo-Dimethanonaphthalene 

 HHDN
 

 NCI-C00044
 

 Octalene 

 Seedrin
 

References 

Davis, K.J. 1965. Pathology report on mice fed dieldrin, aldrin, heptachlor, or heptachlor 

epoxide for two years. Internal FDA memorandum to Dr. A.J. Lehrman, July 19. 

NCI (National Cancer Institute). 1978. Bioassays of aldrin and dieldrin for possible 

carcinogenicity. DHEW Publication No. (NIH) 78-821. NCI Carcinogenesis Tech. Rep. Ser. 

No. 21. NCI-C6-TR-21. 

USEPA (U.S. Environmental Protection Agency). 1980. Ambient Water Quality Criteria for 

Aldrin/Dieldrin. Office of Water. Washington, DC. EPA-440-5-80-019. 

http://water.epa.gov/scitech/swguidance/standards/criteria/upload/2001_10_12_criter 

ia_ambientwqc_aldrindieldrin.pdf. 

USEPA (U.S. Environmental Protection Agency). 1986. Guidelines for Carcinogen Risk 

Assessment. Risk Assessment Forum. Washington, DC. EPA-630-R-00-004. 

http://www.epa.gov/raf/publications/pdfs/CA%20GUIDELINES_1986.PDF. 

USEPA (U.S. Environmental Protection Agency). 1993. Aldrin (CASRN 309-00-2). Integrated Risk 

Information System. Retrieved 08 July 2013. http://www.epa.gov/iris/subst/0130.htm. 

USEPA (U.S. Environmental Protection Agency). 2000. Methodology for Deriving Ambient Water 

Quality Criteria for the Protection of Human Health. Office of Water. Washington, DC. 

EPA-822-B-00-004. 

http://water.epa.gov/scitech/swguidance/standards/upload/2005_05_06_criteria_hum 

anhealth_method_complete.pdf. 

USEPA (U.S. Environmental Protection Agency). 2002a. Estimated Per Capita Fish Consumption 

in the United States. Washington, DC. EPA-821-C-02-003. 

http://water.epa.gov/scitech/swguidance/standards/criteria/health/upload/consumpti 

on_report.pdf. 

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Aldrin 309-00-2 

USEPA (U.S. Environmental Protection Agency). 2002b. National Recommended Water Quality 

Criteria: 2002. Office of Water. Washington, DC. EPA-822-R-02-047. 

http://water.epa.gov/scitech/swguidance/standards/upload/2008_04_29_criteria_wqct 

able_nrwqc-2002.pdf. 

USEPA (U.S. Environmental Protection Agency). 2011. Exposure Factors Handbook: 2011 

Edition. Office of Research and Development. Washington, DC. EPA-600-R-09-052F. 

http://www.epa.gov/ncea/efh/pdfs/efh-complete.pdf. 

USEPA (U.S. Environmental Protection Agency). 2012a. Estimation Programs ͜Σχ͋ι͕̯̽͋ ΋ϢΊχ͋TM 

for Microsoft® Windows, v 4.10. United States Environmental Protection Agency, 

Washington, DC, USA. http://www.epa.gov/oppt/exposure/pubs/episuite.htm. 

USEPA (U.S. Environmental Protection Agency). 2012b. Framework for Human Health Risk 

Assessment to Inform Decision Making. Office of the Science Advisor. Washington, DC. 

EPA-601-D-12-001. http://www.epa.gov/raf/files/framework-document-7-13-12.pdf. 

USEPA (U.S. Environmental Protection Agency). 2014. Estimated Fish Consumption Rates for 

the U.S. Population and Selected Subpopulations (NHANES 2003-2010). Office of Water. 

Washington, DC. EPA-820-R-14-002. 

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