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1 s, methane, and other valuable inorganic and organic chemicals.
2 riod of time while avoiding the use of toxic organic chemicals.
3 ffect the environmental fate of semivolatile organic chemicals.
4 presence of EPFRs in regulating the fate of organic chemicals.
5 ant role in environmental risk assessment of organic chemicals.
6 rcotic toxicity and the chemical activity of organic chemicals.
7 that address the approval and regulation of organic chemicals.
8 process for bioaccumulation of many neutral organic chemicals.
9 rations of salts, alkaline earth metals, and organic chemicals.
10 forces that govern the environmental fate of organic chemicals.
11 enough to control the global distribution of organic chemicals.
12 ish describing the uptake and disposition of organic chemicals.
13 lculate the Globally Balanced State (GBS) of organic chemicals.
14 -term cumulative exposure to metals and some organic chemicals.
15 edict partition coefficients (K) for neutral organic chemicals.
16 inc, cadmium, lead, mercury, and nickel) and organic chemicals (a phthalate and a number of polynucle
17 shown to be important reservoirs for neutral organic chemicals across a wide range of partitioning pr
18 ed here can be expanded to produce important organic chemicals, all through biological activation of
19 ing using a rotating drum impactor (RDI) and organic chemical analysis using direct liquid extraction
20 ticular for solar-energy-driven synthesis of organic chemicals and commodities, moving away from simp
21 -necrosis require incremental amounts of the organic chemicals and increased levels of oxidative stre
24 iptors for numerous environmentally relevant organic chemicals and system parameters for environmenta
28 Initially, SHEDS-HT has been applied to 2507 organic chemicals associated with consumer products and
30 tates the in situ measurement of hydrophobic organic chemicals bioavailability in sediments in terms
31 o has the potential to enhance regulation of organic chemicals by linking results from laboratory tes
33 retrospective risk assessment frameworks for organic chemicals; by doing so, realistic decision-makin
34 hat membrane-water partition coefficients of organic chemicals can be used to predict bioaccumulation
36 ntial TH disruptive contaminants (metals and organic chemical compounds) affect plasma TH levels in f
37 actions of, and biodegradation pathways for, organic chemical compounds, especially those produced by
38 ) models of the distribution of nonionizing, organic chemical concentrations in indoor environments r
39 s are the main sources of pollution for most organic chemicals considered, but north of the Arctic ci
42 ntrations of metals (especially cadmium) and organic chemicals correlated with the presence of tumor
43 enhanced inorganic chemical remediation and organic chemical degradation using various pathway-engin
46 are indicative of an asymmetric influence on organic chemical evolution before the origin of life.
47 y addresses the question whether hydrophobic organic chemicals exerting no toxicity at their solubili
52 potential for bioaccumulation of persistent organic chemicals from sediment useful to prioritize man
56 changes in catalysts and controls of flow of organic chemicals have evolved in the divided space of c
57 was applied to determine the toxicity of 35 organic chemicals, having a wide range of toxicity to fi
58 mass balance model was developed to estimate organic chemical HLB from measured HLT data in mammals.
59 three different AC treatments on hydrophobic organic chemical (HOC) concentrations in pore water, ben
60 oplastic will transfer hazardous hydrophobic organic chemicals (HOC) to marine animals' has been cent
61 ish tests, sorption of 11 highly hydrophobic organic chemicals (HOCs) (log KOW 5.5-7.8) from differen
62 e environmental chemodynamics of hydrophobic organic chemicals (HOCs) are often rate-limited by diffu
63 ly applied for the enrichment of hydrophobic organic chemicals (HOCs) from various types of samples a
64 The binding and speciation of hydrophobic organic chemicals (HOCs) in aqueous solutions were deter
66 o-water fluxes of sediment-bound hydrophobic organic chemicals (HOCs) in the presence of bioturbators
68 ssolved concentration (Cfree) of hydrophobic organic chemicals (HOCs), leading to poorly defined expo
69 solved aqueous concentrations of hydrophobic organic chemicals (HOCs), such as polycyclic aromatic hy
70 quantitative determination of BPA and other organic chemicals (i.e., benzophenone-3, triclosan, para
72 sess aerobic and anaerobic transformation of organic chemicals in aquatic sediment systems and is an
75 s about whether concentrations of persistent organic chemicals in human milk decrease over the course
76 pproach to include occupational exposures to organic chemicals in life cycle impact assessment (LCIA)
78 pids, were used to predict concentrations of organic chemicals in two fish species: rainbow trout (On
79 characterize the equilibrium partitioning of organic chemicals in various environmental and technical
80 3032 measurement end points for 477 discrete organic chemicals including 964 half-lives, 1199 AEs and
81 flowing river water that was spiked with 22 organic chemicals including pharmaceuticals, pesticides
83 The sampler is based on a modified Polar Organic Chemical Integrative Sampler (POCIS) with a weak
84 ompare the conventional pharmaceutical polar organic chemical integrative sampler (POCIS) with modifi
85 te sorbent material (e.g., in a POCIS; polar organic chemical integrative sampler) or to reduce the s
86 the boundary layer compared to that of polar organic chemical integrative samplers (POCIS) deployed s
90 their respective protein products, and other organic chemicals made by the cell create these signpost
91 was done using monitoring data of biota and organic chemicals, mainly pesticides, from five studies
95 ead environmental pollution by inorganic and organic chemicals, novel methods of decontamination and
97 our knowledge, the first risk assessment of organic chemicals on the continental scale comprising 4,
100 tigated the mechanism by which redox cycling organic chemicals, prepared from DEP, induce phase II en
105 our worked and impact intensities for 19,069 organic chemical/sector combinations with confidence int
108 ly reduce the bioavailability of hydrophobic organic chemicals such as polychlorinated biphenyls (PCB
109 the addition of small quantities of certain organic chemicals, such as dimethylsulfoxide (DMSO), bet
110 tors (EFs) for a broad range of semivolatile organic chemicals (SVOCs) from subtropical eucalypt fore
111 se dust extracts and a suite of semivolatile organic chemicals (SVOCs) that are often ubiquitously de
112 an important source of various semivolatile organic chemicals (SVOCs) to the atmosphere including po
113 ent-fluid compositions, varieties of abiotic organic chemical synthesis and extremophile microorganis
116 xhaust particles (DEP) contain redox cycling organic chemicals that induce pro-oxidative and pro-infl
117 To aid in molecular modeling, the use of organic chemicals that mimic key structures of the antag
121 arrier, producing increased accessibility of organic chemicals to the central nervous system; and nit
122 ated for over 35 days for nutrient and trace organic chemical (TOrC) removal from municipal wastewate
124 of such a library for abiotic hydrolysis of organic chemicals under environmentally relevant conditi
125 ) designed to simulate the uptake of neutral organic chemicals under variable temperatures, external
126 ver, detailed understanding of the processes organic chemicals undergo in a glacial system was missin
128 e alloy, Ga(Sbx)N1-x is synthesized by metal organic chemical vapor deposition (MOCVD) for solar hydr
129 low-melting, thermally stable cadmium metal-organic chemical vapor deposition (MOCVD) precursors hav
130 than those of conventional solid zinc metal-organic chemical vapor deposition (MOCVD) precursors.
131 gO(100) substrates at 410 degrees C by metal-organic chemical vapor deposition (MOCVD), and their pha
132 atomic layer deposition) and MOCVD (= metal-organic chemical vapor deposition) processes in material
136 They are grown with a newly developed, metal-organic chemical vapour deposition technique, and show h
139 ystem designed to determine complex volatile organic chemical (VOC) mixtures encountered in indoor wo
140 oot herbivory change the profile of volatile organic chemicals (VOCs) emitted by the host plant; (3)
141 I) model, describing vapor entry of volatile organic chemicals (VOCs) into buildings located on conta
143 er partition coefficients (K(pw)) of neutral organic chemicals were measured using muscle proteins (f
145 ns, often generates a wide range of valuable organic chemicals which find applications in the pharmac
146 nt sink that forests provide for atmospheric organic chemicals which should be considered for emissio
147 oroalkyl acids (PFAAs), a group of synthetic organic chemicals with industrial and commercial uses, a
148 elative change in total mass for hydrophobic organic chemicals with log air-water partition coefficie
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