vvEPA
                              United States
                              Environmental Protection
                              Agency
                                Environmental Research
                                Laboratory
                                Athens GA 30613-7799
                              Research and Development
                                EPA/600/M-89/017  Aug.1989
ENVIRONMENTAL
RESEARCH   BRIEF
      Computer Prediction of Chemical Reactivity—The Ultimate SAR

            Samuel W. Karickhoff.i Lionel A. Carreira,2 Clyde Melton.3 Valeta K. McDaniel.1
                             Andre N. Vellfno,3 and Donald E. Nute3
Introduction
Approximately 70,000 industrial chemicals are listed by
EPA's Office of Toxic Substances. As the evaluation and
management of  the environmental and  human risk
associated with the proliferation of these anthropogenic
chemicals becomes an increasingly urgent social priority,
there accrues a corresponding demand on  physical and
biological scientists and engineers to provide effective
techniques for quantifying their release, fate, and potential
environmental damage.  Historically, Federal health and
safety regulators  (i.e., the U.S. Environmental Protection
Agency and the  Occupational Safety  and  Health
Administration) have relied on field monitoring, toxico-
logical  test data, and  expert scientific knowledge to
condemn or vindicate a given chemical. Recent emphasis,
however, on more quantitative and comprehensive risk/
benefit analyses, coupled with the extension of the
regulators'  "umbrella"  (via the Toxic Substances Control
1 Environmental Research Laboratory, USEPA, Athens, GA 30613-
 7799.
2Chemisry Department, University of, Georgia, Athens, GA 30602.
3Advanced Computational Methods Center, University of Georgia,
 Athens, GA 30602
                Act) over all manufactured chemicals (including those in
                the pre-manufacturing stages) has required the develop-
                ment of more sophisticated  evaluation methods.  These
                methods must be capable of forecasting pollutant
                behavior over wide ranges of environmental conditions,
                often without the benefit of measured data specific to the
                chemical or ecosystem in question.

                Although a wide variety of approaches can be used in
                such judgmental exercises, a knowledge of the relevant
                chemistry of the compound in question is critical to any
                assessment scenario. For volatilization,  sorption and other
                physical processes, considerable success has  been
                achieved in not only phenomenological process modeling
                but also a priori estimation of requisite chemical param-
                eters such as solubilities and Henry's Law constants.<1-3)

                Although considerable progress has been made in pro-
                cess elucidation and modeling  for chemical processes
                such as photolysis and hydrolysises),  reliable estimates
                of the related fundamental chemical constants (i.e., rate
                and equilibrium constants) have been achieved for only a
                small number  of molecular  structures. The values  of
                parameters, in most instances, must  be  derived  from
                measurements or from the expert judgment of specialists
                in that  particular area of chemistry. Parametric values

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have actually been measured for, perhaps, only about one
percent of the chemicals in the OTS inventory.  Because
these measurements may easily cost $20,000 to $100,000
per chemical, estimation techniques  for these  pararqetric
values are very cost-effective. In  any case,  trained tech-
nicians  and adequate  facilities are  not available  for a
measurement effort involving thousands of chemicals^ We
describe here a prototype system  for  the estimation  of
reactivity parameters that will cost the user only a few
minutes of computer time.                          ;

This work  seeks to develop methods  for the  computer
estimation  of fundamental reactivity  parameters strictly
from molecular structure. Although the prototype system,
called SPARC (SPARC Performs Automated Reasoning in
Chemistry), presently deals only with the prediction of UV-
Visible light absorption spectra and pKa, the, techniques
discussed below are being extended to  other  reactivity
parameters  such as  hydrolysis rate constants. | Any
predictive method should  be understood  in terms of the
purpose for which it is conceived and should be structured •
by appropriate operational constraints. The  methods
described  herein  are  intended  for what  migh^ be
characterized as engineering applications in environrrjental
assessments. More specifically they provide:        [
                                                 i
• an a priori estimate of reactivity parameters for dhem-
   ical process models when measured data are unavail-
   able,                                          !
• guidelines for ranking a large  number of  chemical
   parameters and processes in terms of  relevance to the
   question at hand, thus establishing priorities for  meas-
   urement or study,                             I
• an evaluation or screening mechanism  for existing data
   based on expected behavior,  and guidelines for inter-
   preting  or understanding existing data and  observed
   phenomena.                                   ;

The  primary operational  constraint  is that  the  data
available for testing and calibrating predictive theories are
 limited in  both quantity  and quality. This lack ofj data
 recommends a less empirical-that is, more theoretical-
 approach  moderated by  the operational axiom that
 complexity  not exceed  need.  In  addition,  predictive
 capability  should extend to the  entire world  of organic
 chemicals. In particular, the theory should not be crippled
 by the computation and calibration  requirements of| large
 (molecular  weights greater  than  200) polyfunctional
 molecules.                                      j
 Scientific Computing
 Until recently,  scientific computing  consisted  almost
 entirely of mathematical calculations.  These  programs,
 although they often contain  deep  and involved  mathe-
 matics, do not typically express a fully developed scientific
 theory. A scientific computer program, for example,  might
 yield a  solution to  Schrodinger's equation  for  many
 particles using  a self-consistent  approximation method.
 Such scientific computer programs can be thought; of as
 tools or instruments that extend the power of a theory, but
 they are not formulations of a theory.
 The "new wave" computer technology of expert systems
 provides  for imbedding theoretical knowledge as well as
 calculation  algorithms into computer  programs that, in
 principle, can  shorten  the distance between  scientific
 theory  and computer implementation.  In  most scientific
 applications to date, however, expert systems have fallen
 short .of actual theory implementation, relying heavily on
• pattera matching or correlational inferencing in  predictive
 strategy.  Also, most of the current  expert  systems are
 oriented to  a specific application and are targeted primarily
 to expert users  within a  particular scientific discipline.
 Interested  readers should consult recent reviews by
 Gray<9> and Pierce and Hohne(10> in which existing  expert
 systems  for molecular structure  elucidation,  chemical
 synthesis, and molecular design are described.

 . In the field  of organic chemistry, an extensively developed
 theoretical  basis'exists already for  estimating  chemical
 reactivity  from  molecular  structure. This theoretical
 knowledge base  refers to the  body of  facts,  general-
 izations,  models,.laws, and theories that form the basis for
 mechanistic reasoning  in physical organic chemistry.
 Mechanistic reasoning refers to  the process of analyzing a
 chemical change  in terms of more elementary component
 processes, such as critical motions of certain electrons or
 nuclei  or  sequential  events through  which  the  trans-
 formation  proceeds. (For indepth descriptions, readers
 may consult physical organic chemistry texts such  as that
 of Lowry and Richardson.<11>)

 The goal for our expert system  is to capture the reasoning
 process  that an organic chemist might undertake in reac-
 tivity analysis. The approach primarily involves deductive
 reasoning  and is theory/mechanism  oriented.  Computa-
 tional  procedures are based on  existing mathematical
 models of  theoretical chemistry.
  Chemical Modeling

  Chemical properties describe  molecules in transition, that
  is, the conversion  of a reactant molecule to a  different
  state  or structure.  For, a  given  chemical property, the
  transition of interest may involve  electron redistribution
  within a single  molecule  or bimolecular union to form a
  transition  state  or distinct product.  The behavior of
  chemicals  depends on  the  differences in  electronic
  properties of the initial state of the system and the state of
  interest. For example, a light absorption spectrum reflects
  the differences in energy  between the ground  and excited
  electronic states of a given molecule. Moreover, chemical
  equilibrium—thus chemical equilibrium constants—de-
  pends on  the energy differences between the  reactants
  and  products. Reaction rates, on  the  other  hand, may
  depend on the  energies of a transition  state relative to
  either reactants or products.

  For  the reactions  addressed in SPARC, these  energy
  differences are  extremely  small compared  to  the total
  binding energies of the reactant involved. This presents a
  problem for ab initio  computational  procedures  that
  calculate absolute energy values. Computing the relatively
  small energy differences needed  for  the  analysis of
  chemical  reactivity from  absolute energies   requires

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extremely accurate  calculations.  Although achievable for
small subclasses  of molecules for certain  reactivity
parameters,  these  methods cannot provide the  major
computing thrust for  SPARC  considering the projected
scope and aforementioned constraints.

There are, however, methods known under the general
heading of "perturbation theories," that make it possible to
calculate energy differences directly. These theories treat
the final  state as a  perturbed initial  state and the energy
differences,  then,  are  determined  by  quantifying the
perturbation.

Perturbation  methods can  be used not only  to predict
reactivity of a  given chemical but also  to  compute
differences in reactivity for "similar" reactants.  Although
they  provide potentially  more accurate  and  simpler
computations, the  use of  perturbation  methods requires
considerable circumspection. One must be careful to:

• define the boundary conditions of  an algorithm's
   validity,
• choose appropriate reference states for calibration and
   extrapolation, and
• define, in  terms  of molecular  structure, the meaning of
   terms like "chemical similarity."

These perturbation  methods are ideally  suited  for expert
system  application due to their extreme  flexibility and
computational  simplicity.  The  requisite conditions  for
applicability, as well as  the selection of appropriate
reference structures or reactions, can be easily built into
the computation control portion of the expert system.


 SPARC Computational  Procedures

 An indepth description of  SPARC  procedures  is beyond
 the scope of this brief. The following, however, is a limited
 description  of  the  logic of our approach to  chemical
 parameter prediction and  provides an  overview  of  the
 reasoning  and computational procedures  currently
 incorporated in SPARC.

 The  basic  philosophy  is  not to compute  any chemical
 property from   "first  principles." Rather, it is  to  utilize
 directly the extensive  knowledge  base of  organic
 chemistry. Organic chemists have established the types  of
 structural groups or atomic arrays that impart certain types
 of reactivity and have described, in "mechanistic"  terms,
 the effects  on  reactivity  of other  structural constituents
 appended to the site of reaction.

 To  encode this knowledge base, a classification scheme
 was developed  that defines the role  of  structural
 constituents  in  effecting  or modifying  reactivity.
  Furthermore, models have been developed that quantify
 the various  "mechanistic"  descriptions  commonly utilized
  in  structure-reactivity analysis,  such  as  induction,
  resonance, and field effects.  SPARC execution  (Figure  1)
  involves the classification  of molecular  structures (relative
  to a particular reactivity of interest) and the selection and
  execution of appropriate "mechanistic"  models to quantify
  reactivity.
The computational approaches in SPARC are a blending of
conventional linear free energy  theory (LFET),  structure
activity  relationships (SAR), and  perturbed molecular
orbital (PMO) methods. In general, SPARC utilizes LFET to
compute thermal  properties  and PMO theory to describe
quantum  effects such as  delocalization  energies  or
polarizabilities  of  n electrons. In reality, every  chemical
property involves  both quantum and thermal contributions
and  necessarily requires  the use  of both perturbation
methods for prediction.  These  approaches have  been
extensively  developed and  utilized in physical  organic
chemistry.  For detailed  descriptions, readers should
consult  texts by Leffler and Grunwald(12> and Hammett<13>
on LFET and SAR, Dewar(14> and Dewar and Dougherty!15)
on PMO theory, and the reviews of Taft et a/.(16> on SAR
applications.
Structure Classification

Reactivity  assessment  in SPARC  begins with locating
potential sites within the molecule for a particular reaction
of interest. These reaction sites, which are termed reaction
centers (C), are in general the smallest subunit(s) to which
the reactivity  of interest can be ascribed. Any molecular
structure  appended to C  is  viewed  as a  "perturber,"
denoted P. All reactions to be addressed in SPARC (from
light  absorption to hydrolysis) are analyzed in terms of
some critical equilibrium component:
PCn
                     f(AE)
                                  PC,
                       (D
 where C0 and Cf denote initial and "final" states  of the
 reaction center C, P is the "perturber"—the structure that
 is  presumed  unchanged  by the reaction, fA(E) denotes
 some reaction parameter of interest that  is a function  of
 the energy change (AE) of the reaction. For example, the
 ionization of phenol is described by:
           OH
                       (2)
 where C0, Cf and P are -OH, -O— and the phenyl group,
 respectively.

 For light absorption, C0 and Cf are ground and excited
 states of the  reaction center and f(AE) is  the intensity of
 light absorption as a function of incident light energy (that
 is, the absorption spectrum). For reaction kinetics, C0 and
 Cf may  denote the initial and  transition  states  of  the
 reaction  center, and f(AE) is the rate constant expressed
 as a function of the energy  required for achieving  the
 transition state.

 The  energy change is expressed in terms  of contributions
 of factored structural components. For thermal properties,
               AE = AEn
8P (AEC
                                       (3)

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  User Input
    Molecular Entry System:
      —Smites
      —Molecular Editor

    Reactivity Parameter Type:
      —Absorption Spectra
      -pKa

    Reaction Conditions
      —Solvent
      —Temperature
                                        Internal Molecular
                                      Structure Representation
                                          —Prolog Database
                                            Structural Classification
                                                —Reaction Centers
                                                —Perturbers
                                            Process Descriptors
                                      Algorithm Selection and Execution
     Output
       Graphics Display:
         —Spectral Plot
       Numerical Output
         —pKa Values
                                           Parameter Base
   Output Display:
     —Spectral Plots
     —Numerical Values
 Rgure 1.    SPARC overview.
                                                 abti<
where AEc describes the intrinsic behavior of the reaction
center,  and 6P(AEC)  denotes some perturbation derived
from  the  appended structure,  P. Changes in  localized
bonding energies  are incorporated  in  AEC  andj are
assumed unchanged by P. For each reaction type, SPARC
catalogues  reaction  centers and appropriate  charac-
terization  data,  f(AEc). These  reference data  are! not
calculated a priori, but are inferred directly from measured
data.  Rgure 2 contains sample reaction centers for acid or
base  ionization  constants  (pKa's)  and  UV-Visible  [light
absorption.  SPARC computes  reactivity  perturbations,
8p(Reac) that are then used to "correct" the  intrinsic
behavior of the  reaction  center for the  compound in
question.                                          !
                                                  I
To facilitate quantitative modeling, 8p(Reac) is expressed
in terms of potential "mechanisms" for interaction of P, and
C.
      8P (Reac) = 8e (Reac) + 8,(Reac)
                                                   (4)
where subscripts  e and r denote  electrostatic |and
resonance  interactions, respectively.  Electrostatic ifiter-
actions derive from local  electric dipoles or charges [in  P
(fixed or induced) interacting with charges or dipoles |n C.
Because 8p(Reac)  describes changes  in  the reaction
C0-»Cf effected by P, 8e(Reac)  represents the difference
in the electrostatic interactions of P with the two states, C0
versus C(. Resonance  interactions involve  the delocal-
ization of n electrons into or out of C,  but again, 8r(Reac)
describes the change in electron delocalization accom-
panying  the  reaction. Additional  perturbations  include
specialized interactions  of  structural elements  of P
contiguous to the reaction center  such as H-bonding or
steric blockage  of access to  C  for  another molecule
(solvating or reacting).

The following examples are indicative of the extrapolation
capability of SPARC. Figure 3  shows  calculated and
measured  UV-Visible absorption  spectra of  sexiphenyl
isomers, each of which was  calculated as  a  "perturbed"
benzene. The para isomer shows extended n conjugation
throughout the six-membered  ring, whereas  the  meta
isomer shows only pair-wise ring  coupling. In the  ortho
isomer, steric  twisting of the  essential  single  bonds
removes, to a large extent, ring coupling. These spectra
reflect the ability of SPARC to consider both electrometric
and steric factors in resonance perturbations.

Figure 4 shows  predicted and  measured  pKa's for  the
reaction center, -OH,  in a variety of molecular structures.
These compounds  demonstrate  the extendability  of
SPARC procedures to inorganic compounds and to both
aliphatic and aromatic organic compounds. Figure 5 shows
similar information for the phosphono reaction center.


Model Verification and Testing

In chemistry, as  with all physical sciences, one can  never
determine  the  "validity" of any  predictive model with
absolute certainty. This is a direct consequence  of  the
empirical nature of the science. The closest one can get to
"truth" in chemistry is to make use of the established laws

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     Light Absorption
II -II* - rigid structures
- ethylene
- benzene
- napthalene
ri - n* - NR2
-OH
-SH
- N (In ring)
- S (In ring
-C = O
-C = S
-C-NH
Acids - OH
-SH
-CO2H
-PO2H
1
- B(OH)2
-SO2H
- SeO3H
- AsO2H
1
Bases - NR2
- N (In ring)
-C = N -
-C = O
 Figure 2.   Reaction centers for light absorption  and
            acid/base equilibrium.
and  theories,  whose  validity derives not  from logic but
from experience, having  withstood exhaustive challenges
or attempts to  falsify.  This  established theoretical
knowledge provides our  best description  of  what the
molecular world is really like. Because SPARC is expected
to predict reaction parameters for processes for which little
or no relative  data exist for corroboration, "validity"  must
derive from  the efficacy of the model  constructs in
"capturing"  or reflecting the  existing knowledge  base of
chemical reactivity.

In every aspect  of SPARC development, from choosing
the  programming  environment  to  building   model
algorithms  or  rule  bases,  testability was  an  important
criterion. As discussed earlier, the capability to extrapolate
and/or to avoid  situation-specific or  ad hoc  descriptions
was  a primary goal for  SPARC. The  basic  mechanistic
models were  designed  and parameterized so as to be
portable, in principle, to any type of chemistry or chemical
structure. This extrapolatability  enhances testability  in
several important ways. First, as the diversity of structures
and the chemistry  that is addressable increases, so does
the opportunity for failure.  More importantly,  however, in
testing against the theoretical  knowledge of  reactivity,
specific  situations can  be chosen that offer specific
challenges.  This is  particularly  important  when  testing
performance in areas where existing data are limited  or
where additional data collection may be required. Finally,
this expanded prediction capability allows one to choose,
for exhaustive testing, the  reaction parameters for which
large and reliable data sets do  exist to test against.  Test
data  sets are presently being  encoded, including  UV-
Visible absorption  spectra  (about  5000 compounds) and
ionization  pKa's  (about  18,000 compounds). These
unbiased and unscreened data sets will  provide an
exhaustive test of performance covering a broad domain of
chemistry.

Is SPARC  verifiable? SPARC was designed  to optimize
falsifiability. A more pertinent question from  a pragmatic
viewpoint is what happens  when SPARC fails? In general,
failures to predict  derive not by  happenstance, but  from
errors or inadequacies  in  conceptualization  or theory
implementation.  Again, one must resort to the  theoretical
knowledge base of chemical reactivity to determine  the
source(s) of failure. The "mechanistic" output of SPARC
should aid  in the process. In addition, the modular design
                                                    p - Sexiphenyl
                                                    Sexiphenyl  isomers
                   37500
                                     Frequency (cm'1)
                                                               20000
  Figure 3.    Predicted (solid lines) and measured spectra of Sexiphenyl isomers.

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    Inorganic and Organic reaction with the Reaction Center, -OH
                                                                                                       o
                                                                                                       H
                            EtOH
                            16.0(15.9)
           Me OH
             15.5(15.5)
IJOBr
H.O
14.0(14.0)
               a  9.4(9.4)
               P  9.5(9.5)

 Figure  4.    Predicted and measured (values in paren-
             theses) pKa's for compounds containing the
             reaction center, -OH. For example, the phony!
             group and  -OH react to produce phenol
             (indicated by*) with a predicted value of 10.0,
             which compares with the measured  value of
             10.0. Further reaction with bromine produces
             o-, m- and p- bromophenol to give predicted
             and measured values as  shown. A typical
             inorganic addendum is OH with the reaction
             center to produce H202 (indicated by #)  for a
             predicted pKa of 11.7 as compared to the
             measured pKa of 11.6. Note: there are  no
             measured pKa values for the various bromine-
             substituted benzylalcohols (indicated by @).


and  programming environment  of SPARC  facilitates
modifying or adding to model algorithms or the rule bases.
This  provides,  we  hope,  for  coherent  growth  or
advancement in predictive capability. In this  capacity, the
SPARC approach also can serve as  a research tool for
resolving  conflicting  viewpoints  or perhaps ultimately
advancing the field of reactivity description.
   Projection

   The  methods described  above predict UV-Visible light
   absorption  spectra,  ionization pKa's,  and  hydrolysis
   reaction rates. The prototype computer program currently
   runs  on  a  widely  used  minicomputer  and  uses
   commercially  available  Prolog and Fortran compilers.
   Plans are  being developed for a  PC version.  Future
   development in the modeling will include:

   For Light Absorption Spectra—
   •  expand  the reaction  center database  to  include all
      commonly encountered "rigid" n structures,
                                                                  Inorganic and organic reaction with the Reaction Center,  . p . O - H
                                                                        HPO4-
                                                                    12.2(12.0)
                                                                                        NHjPO3H2
                                                                                           3.0(3.0)
                                                                                                 CH3PO3HZ
                                                                                                    2.7(2.4)
                                                                  H3PO4

                                                               2-1(2.1)
                                                                                              CH3PO3H-
                                                                                                7J (7.1-7.77)
                                                               2.1 (1.9)
                                                                                                   
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This expert system should be a boon to any Agency Office
or Region, state or other environmental group needing to
predict the concentration of a pollutant  in a  particular
environment  for  exposure assessment.  It should  be
valuable  to Agency  regulators  in their modeling  efforts
relative to  the  assessment of  land disposal  of wastes,
compliance monitoring,  development of remedial  action
plans, implementation  of  premanufacturing  notice
regulations, or in any area where the chemical reactivity of
pollutants is important in exposure prediction. SPARC can
estimate  reactivity parameters  at  less cost, with greater
accuracy, and with a broader scope than any conventional
technology.


References

 1.  Lyman, W. J.,  W. E.  Reehl,  and  D.  H.  Rosenblatt.
    1982. Handbook  of Chemical  Property  Estimation
    Methods:  Environmental Behavior  of Organic
    Chemicals.  McGraw-Hill, New York, NY.

 2.  Yalkowski, S.  H. and S.  C. Valfani.  1980. Solubility
    and  Partitioning  I: Solubility  of Non-electrolytes  in
    Water. Pharmaceutical So/., 69:912-913.

 3.  Leo,  A. J. 1975. Calculation of Partition Coefficients
    Useful in  Evaluation of the Relative Hazards of Various
    Chemicals in the Environment. /. J. C. Symposium on
    Structure Activity Correlations in Studies  of Toxicity
    and  Bio-concentrations  with Aquatic Organisms.
    (Veith,  G. D.,  ed.),  International Joint Commission,
    Windsor,  Ontario.

 4.  Zepp,  R. G.  1982. Experimental Approaches  to
    Environmental Photochemistry. In: Handbook of Envi-
    ronmental Chemistry (Hutzinger, O.,  ed.),  Vol. 2(B)
    Springer-Verlag, New York, NY, pp. 19-42.
 5.  MacKay,  D.,  A.  Bobra,  W.  Y.  Shiu,  and  S.   H.
    Yalkowski. 1980. Partition Coefficients.  Chemosphere,
    9:701-711.

 6.  Zepp, R.  G. and D. M. Cline.  1977. Rates of Direct
    Photolysis in the Aquatic Environment. Environmental
    Science and Technology, 11:359-366.
 7.'Wolfe,  N.  L, R. G.  Zepp,  J.  A. Gordon,  G.  L.
    Baughman, and  D. M.  Cline.  1977. Kinetics  of
    Chemical Degradation of Malathion in Water. Environ-
    mental Science and Technology, 11:88-100.
 8. Smith, J. L, W. R. Mabey, N. Bohanes, B. B. Hold, S.
    S. Lee,  T.  W. Chou, D. C. Bomberger,  and  T.  Mill.
    1978. Environmental Pathways of Selected Chemicals
    in Freshwater Systems: Part II, U. S. Environmental
    Protection Agency, Athens, GA, EPA/600/7-78/074.
 9.  Gray, Neil A. B. 1986. Computer Assisted Elucidation.
    Wiley and Sons, New York, NY.
10. Pierce, T. H.  and B. A. Hohne (eds.).  1986. Artificial
    Intelligence Applications in  Chemistry, American
    Chemical Society,  Washington,  DC,  Symposium
    Series, No.  306.
11. Lowry, T. H. and K. S. Richardson.  1987. Mechanisms
    and Theory in Organic  Chemistry, 3rd ed., Harper &
    Row, New York, NY.
12. Leffler,  J.  E. and  E.  Grunwald.  1969. Rates  of
    Equilibria of Organic Reactions. Wiley and Sons,  New
    York, NY.
13. Hammett, L.  P. 1970.  2nd ed.  Physical  Organic
    Chemistry, McGraw Hill, New York,  NY.
14. Dewar, M. J. S. 1969. The Molecular Orbital Theory of
    Organic Chemistry, McGraw Hill, New York, NY.
15. Dewar, M. J. S. and R. C. Dougherty. 1975. The PMO
    Theory of  Organic  Chemistry. Plenum  Press, New
    York, NY.
16. Taft,  R.  W.  (ed.). 1987. Progress  in Organic Chem-
    istry, Vol. 16. Wiley and  Sons, New  York, NY.
17. Karickhqff,  S. W., Lionel  A. Carreira, Clyde  Melton,
    Valeta K. McDaniel,  Andre N.  Vellino, and Donald  E.
    Nute.  Predicting  Chemical Reactivity By Computer,
    Part I: Approach. Submitted for publication. 1989.
18.  Karickhoff,  S. W., Lionel  A. Carreira, Clyde  Melton,
    Valeta K. McDaniel,  Andre N.  Vellino and Donald  E.
    Nute.  Predicting  Chemical Reactivity by Computer!
    Part  II:  UV-Visible  Light  Absorption.  Submitted  for
    publication.  1989.
19.  Karickhoff,  S. W., Lionel  A. Carreira, Clyde  Melton,
    Valeta K. McDaniel,  Andre N.  Vellino, and Donald  E.
    Nute. Predicting  Chemical Reactivity By Computer,
    Part  III:  lonization pKa.  Submitted for  publication.
    1989.

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Environmental Protection
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