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1 provided by the Massachusetts Department of Environmental Protection.
2 shaping attitudes toward the environment and environmental protection.
3 tively correlated with the area under strict environmental protection.
4 safety regulations, and limited measures for environmental protection.
5 nergy conversion and storage, as well as for environmental protection.
6 pplications such as occupational exposure or environmental protection.
7 creasing global needs for sustainability and environmental protection.
8 due to their advantages in energy saving and environmental protection.
9 entives for resource efficiency, equity, and environmental protection.
10 play to meet the increasing global needs for environmental protection.
11 this diet shift can be an effective tool in environmental protection.
12 om the viewpoints of both sustainability and environmental protection.
13 als in the context of emission reduction and environmental protection.
14 een sustainable development goals, including environmental protection.
15 t in guideline values that can be useful for environmental protection.
16 remediation) of nutrient-rich wastewater and environmental protection.
17 e.g., nitrogen oxide emission abatement for environmental protection.
19 mug L(-1)) as well as by analyzing the U.S. Environmental Protection Agency (EPA) 552.2 CRM (certifi
20 s of ground-based measurements from the U.S. Environmental Protection Agency (EPA) Air Quality System
21 with the metal, it has been mandated by the Environmental Protection Agency (EPA) and Occupational S
22 ts show that current inventories from the US Environmental Protection Agency (EPA) and the Emissions
24 Verhaar prediction of toxicity MOA, the U.S. Environmental Protection Agency (EPA) ASsessment Tool fo
26 ted Risk Information System (IRIS), the U.S. Environmental Protection Agency (EPA) completed a toxico
28 During emergencies in the United States, the Environmental Protection Agency (EPA) currently recommen
30 ro exposure to inorganic arsenic at the U.S. Environmental Protection Agency (EPA) drinking water sta
32 sruption has driven the creation of the U.S. Environmental Protection Agency (EPA) Endocrine Disrupto
34 ment since the guideline value set by the US Environmental Protection Agency (EPA) for inorganic merc
35 e current standard method recommended by the Environmental Protection Agency (EPA) for the detection
36 ative inventories based on the United States Environmental Protection Agency (EPA) Greenhouse Gas Inv
37 then 36,000-fold higher than reported by the Environmental Protection Agency (EPA) Greenhouse Gas Rep
39 ted Risk Information System (IRIS), the U.S. Environmental Protection Agency (EPA) has evaluated the
41 Both vehicles were exercised over double Environmental Protection Agency (EPA) Highway fuel econo
43 1173 chemicals that the United States (U.S.) Environmental Protection Agency (EPA) identified as bein
45 e health end point used by the United States Environmental Protection Agency (EPA) in its benefits an
47 s designed to be consistent with the 2016 US Environmental Protection Agency (EPA) Inventory of US Gr
49 the Toxic Substances Control Act (TSCA), the Environmental Protection Agency (EPA) is required to per
50 ocrine Disruptor Screening Program, the U.S. Environmental Protection Agency (EPA) led two worldwide
54 016 Lautenberg amendments, the United States Environmental Protection Agency (EPA) must evaluate chem
55 d, burned, and emissions sampled at the U.S. Environmental Protection Agency (EPA) Open Burn Testing
59 s of gross beta activity, collected at seven Environmental Protection Agency (EPA) RadNet monitors lo
60 n concentrations (>200 mug/L) well above the Environmental Protection Agency (EPA) recommended "do no
61 the Johnson-Ettinger model (JEM), which the Environmental Protection Agency (EPA) recommends as a sc
63 ociations exist at levels below the new U.S. Environmental Protection Agency (EPA) standards (12 mug/
65 dous air pollutants (HAPs) identified by the Environmental Protection Agency (EPA) that are also pres
66 ration (EIA) was combined with data from the Environmental Protection Agency (EPA) to explore ways in
67 summarizing relevant findings from the U.S. Environmental Protection Agency (EPA) ToxCast high-throu
68 increasing scientific engagement in the U.S. Environmental Protection Agency (EPA) ToxCast initiative
69 of magnitude larger than reported to the US Environmental Protection Agency (EPA) Toxics Release Inv
70 rst group of pesticides reviewed by the U.S. Environmental Protection Agency (EPA) under the new law.
71 nds with alternative methodologies, the U.S. Environmental Protection Agency (EPA) used in vitro data
75 looked to information contained in the U.S. Environmental Protection Agency (EPA)'s VI database for
76 he U.S. Department of Energy (DOE), the U.S. Environmental Protection Agency (EPA), and the U.S. Depa
77 than a similarly adjusted total from the US Environmental Protection Agency (EPA), but overlaps EPA'
78 xposure (230 mg L(-1)), stipulated by the US Environmental Protection Agency (EPA), in the next 50 y
79 air pollutants (HAPs) identified by the U.S. Environmental Protection Agency (EPA), not including ozo
81 t level (MCL) suggested by the United States Environmental Protection Agency (EPA), the SPR biosensor
82 aximum contaminant level of 4 ppm set by the Environmental Protection Agency (EPA), we have investiga
83 ial nanofiller effects on the profiles of 16 Environmental Protection Agency (EPA)-priority polycycli
89 nd high-throughput analysis of United States Environmental Protection Agency (U.S. EPA) 16 priority p
91 o potential regulations by the United States Environmental Protection Agency (U.S. EPA) regarding the
92 s) for drinking water as defined by the U.S. Environmental Protection Agency (U.S. EPA) were used to
97 h annual mean emissions reported to the U.S. Environmental Protection Agency (USEPA) and the Californ
98 l indicator recommended by the United States Environmental Protection Agency (USEPA) for water-qualit
99 on cancer risk values that exceeded the U.S. Environmental Protection Agency (USEPA) health-based acc
102 nes in Europe, and in 2007 the United States Environmental Protection Agency (USEPA) recommended BLM-
105 rs of magnitude lower than the United States Environmental Protection Agency (USEPA) tolerance limit
106 lic aromatic hydrocarbons (PAHs) on the U.S. Environmental Protection Agency (USEPA)'s "PAH-34" targe
107 rs of magnitude lower than the United States Environmental Protection Agency (USEPA)-defined limit (1
108 variability in SC, [Cl], and exceedances of Environmental Protection Agency [Cl] criteria using near
109 h Council recently recommended that the U.S. Environmental Protection Agency adopt the concept of "su
110 nt air pollutants were collected from Taiwan Environmental Protection Agency air monitoring stations.
111 our study area were in compliance with U.S. Environmental Protection Agency air pollution standards;
112 ng air pollution data obtained from the U.S. Environmental Protection Agency air quality monitoring n
113 y summertime days between 2005 and 2014 that Environmental Protection Agency Air Quality System O3 mo
115 t is a decision-making tool used by the U.S. Environmental Protection Agency and other governmental o
116 iple large databases, including those of the Environmental Protection Agency and the Department of Ve
118 exposure thresholds recommended by the U.S. Environmental Protection Agency and the European Food Sa
119 workshop, which was cosponsored by the U.S. Environmental Protection Agency and the National Institu
120 the NRC report was commissioned by the U.S. Environmental Protection Agency and the National Institu
122 d air pollution data were collected from the Environmental Protection Agency and Weather Warehouse da
123 perimental Use Permit from the United States Environmental Protection Agency approved a pilot field t
124 Program and under consideration by the U.S. Environmental Protection Agency are fully achievable.
125 y factors (PEFs) developed by the California Environmental Protection Agency are then applied to dete
126 y or Sustainable Chemistry is defined by the Environmental Protection Agency as "the design of chemic
128 pected from pollution changes using the U.S. Environmental Protection Agency Benefits Mapping Analysi
129 e concentration is well below the California Environmental Protection Agency chronic exposure limit (
130 tered at concentrations near or below the US Environmental Protection Agency chronic Fe criterion (1.
134 re closely aligned with criteria of the U.S. Environmental Protection Agency derived from epidemiolog
137 , 2 to 3 orders of magnitude greater than US Environmental Protection Agency estimates for this opera
138 ese spatially resolved damage estimates with Environmental Protection Agency estimates of water quali
139 mpiled biomonitoring and toxicity data, U.S. Environmental Protection Agency exposure predictions, an
141 06 records of fuel economy tests by the U.S. Environmental Protection Agency for 2013 model year vehi
142 publicly available data at the United States Environmental Protection Agency for chemical-manufacturi
143 ance standards recently proposed by the U.S. Environmental Protection Agency for limiting CO2 emissio
144 concentration of Hg recommended by the U.S. Environmental Protection Agency for the issuance of fish
145 , which is lower than that estimated by U.S. Environmental Protection Agency for the same period (0.1
146 r than the maximum level established by U.S. Environmental Protection Agency for water ingestion.
148 tal Panel on Climate Change (IPCC); (2) U.S. Environmental Protection Agency Greenhouse Gas Reporting
150 m nitrosamines in urban PM exceeded the U.S. Environmental Protection Agency guideline of 1 excess ca
151 f detection of 1.93 uM, below that of the US environmental protection agency guidelines (5.37 uM), wi
152 g concentrations do not exceed United States Environmental Protection Agency guidelines for the low e
158 ewater treatment plants by the United States Environmental Protection Agency in its 2001 national sew
164 is 5 orders of magnitude lower than the U.S. Environmental Protection Agency limit for Cu(2+) in drin
165 sensor capable of detecting lead at the U.S. Environmental Protection Agency limit for paint (5000 pp
166 ater contaminant concentrations exceeded the Environmental Protection Agency limits for discharging t
170 ed to water quality criteria, including U.S. Environmental Protection Agency MCLs and "human health c
171 ymerase chain reaction (qPCR) assays of U.S. Environmental Protection Agency Methods 1611 and 1609 bu
172 nd risk of disability occur below the annual Environmental Protection Agency National Air Quality Sta
173 ethod, which was the basis for previous U.S. Environmental Protection Agency national risk assessment
176 opulation intakes exceeding the current U.S. Environmental Protection Agency reference dose of 0.1 mu
177 xposure for young children exceeded the U.S. Environmental Protection Agency reference doses for BDE-
178 e than an order of magnitude lower than U.S. Environmental Protection Agency reference doses, cumulat
181 Inorganic constituents regulated by the U.S. Environmental Protection Agency remained below their res
184 otal concentrations up to six times the U.S. Environmental Protection Agency safe drinking water limi
185 itized by the European Union and/or the U.S. Environmental Protection Agency showed that the PAH CALU
186 aphy and mass spectrometry according to U.S. Environmental Protection Agency standard procedures.
189 est Supersite, a monitoring site of the U.S. Environmental Protection Agency Supersites ambient air m
191 ative human health effects prompted the U.S. Environmental Protection Agency to issue lifetime drinki
192 es the daily intake levels exceeded the U.S. Environmental Protection Agency Tolerable Daily Intake (
193 in agriculture were recently stopped by the Environmental Protection Agency under false scientific p
194 ility-scale data newly collected by the U.S. Environmental Protection Agency was processed to produce
195 2 y of life (F2YL), using data from the U.S. Environmental Protection Agency's (EPA's) Air Quality Sy
197 ans (C. elegans) was used to screen the U.S. Environmental Protection Agency's (EPA's) ToxCast Phase
198 -MARKAL model with a modified version of the Environmental Protection Agency's (EPA) 9-region databas
201 1534 km(2) contained [U] >30 mug/L, the U.S. Environmental Protection Agency's (EPA) Maximum Contamin
202 r DEHP in 39 individuals were above the U.S. Environmental Protection Agency's (EPA) reference dose (
205 and PFOA were removed to below United States Environmental Protection Agency's (USEPA's) health advis
207 fic evidence that has emerged since the U.S. Environmental Protection Agency's 2009 Endangerment Find
208 3 and health effects were identified in U.S. Environmental Protection Agency's 2013 Integrated Scienc
209 s 0.04 in a million, which is below the U.S. Environmental Protection Agency's acceptable risk level.
210 nal air pollutant measures were based on the Environmental Protection Agency's Air Quality System dat
211 stimates based on data derived from the U.S. Environmental Protection Agency's Air Quality System dat
212 ter <=2.5 um (PM(2.5)) was obtained from the Environmental Protection Agency's Air Quality System.
214 s an emerging contaminant in the most recent Environmental Protection Agency's candidate contaminant
216 eater (95% cr int: 1.7x, 8.7x) than the U.S. Environmental Protection Agency's current greenhouse gas
217 ozone and PM2.5 for 2001-2008 from the U.S. Environmental Protection Agency's down-scaled estimates
218 ation from 5 ppm to 1 ppb, lower than the US Environmental Protection Agency's drinking water limit (
219 nd total dissolved solids (TDS) exceeded the Environmental Protection Agency's Drinking Water Maximum
221 man exposures predicted in the United States Environmental Protection Agency's ExpoCast program.
222 re 90% larger than estimates based on the US Environmental Protection Agency's Greenhouse Gas Invento
223 5% confidence interval) compared to the 2012 Environmental Protection Agency's Greenhouse Gas Invento
224 ained significant for PM2.5 levels below the Environmental Protection Agency's health-safety limit (1
225 ts the current 70 ng/L of PFOA and PFOS U.S. Environmental Protection Agency's lifetime health adviso
226 As at 0, 500x, 1,000x, or 2,000x of the U.S. Environmental Protection Agency's maximum contaminant le
227 f volatile organic compounds, well below the Environmental Protection Agency's maximum contaminant le
228 ured from several monitoring sites by the US Environmental Protection Agency's monitoring network.
229 and predicted emission rates using the U.S. Environmental Protection Agency's MOVES model was also a
230 ngation in populations protected by the U.S. Environmental Protection Agency's National Ambient Air Q
231 iences/National Toxicology Program, the U.S. Environmental Protection Agency's National Center for Co
232 tem optimization model is used with the U.S. Environmental Protection Agency's nine-region database t
234 s near 40 ng/m(3), which was higher than the Environmental Protection Agency's Reference Concentratio
235 pact categories defined by the United States Environmental Protection Agency's Tool for the Reduction
237 12, the facilities that reported to the U.S. Environmental Protection Agency's Toxic Release Inventor
238 pper, manganese, or lead (as reported to the Environmental Protection Agency) and counties with no/lo
240 collection method used by the United States Environmental Protection Agency, and delta(15)N-NOx was
241 describe its current application at the U.S. Environmental Protection Agency, and point out how it co
242 gation Management Information System, the US Environmental Protection Agency, and the National Climat
243 the National Institutes of Health, the U.S. Environmental Protection Agency, and the U.S. Centers fo
244 blished by the World Health Organization and Environmental Protection Agency, and whether implementat
245 ical manufacturing data reported by the U.S. Environmental Protection Agency, as well as other publis
247 of 50 microg/kg day set by the United States Environmental Protection Agency, during adolescent devel
269 the complementarities and trade-offs between environmental protection and biofuel development objecti
272 t in a range of areas, including healthcare, environmental protection and energy-related technologies
273 n social policies may contribute to stronger environmental protection and higher environmental qualit
275 put soils at the centre of policy supporting environmental protection and sustainable development.
276 ims at reconciling economic development with environmental protection and sustainable resource use.
277 es applied, emphasis on biodegradability and environmental protection, and integrated pest- and pesti
278 tion, improved programs of public health and environmental protection are needed in countries at ever
279 five decades reveal significant triumphs of environmental protection, but also notable failures, whi
280 irable for the purpose of nuclear safety and environmental protection, but currently not achievable g
281 n filters from the Connecticut Department of Environmental Protection for six cities in Connecticut.
286 solves practical tasks of geological survey, environmental protection, medicine, industry, agricultur
287 ny energy technologies, emissions reduction, environmental protection, mining accident prevention, ch
289 domain of governmental agencies involved in environmental protection, occupational safety, and trans
290 apeutic drugs, as well as in food safety and environmental protection operations is demonstrated.
291 May 19, 2011 the Pennsylvania Department of Environmental Protection (PADEP) requested drilling comp
294 in medical diagnostics and food safety, for environmental protection, process control, wastewater tr
296 Pennsylvania, the Pennsylvania Department of Environmental Protection requires that all water sources
297 talise on investments that societies make in environmental protection that provide ancillary benefits
298 type constitutes genetic risk and allows for environmental protection, thereby providing options for
299 need to be reevaluated to afford appropriate environmental protection under future conditions of OA.
300 holarly views on the commitment of states to environmental protection when energy development opportu