EPA-540/9-75-018
February 1975
Evaluation of the Possible Impaet
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Research and Development Activilies
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of Pesticide Manufacturers
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Office of Pesticide Programs
Office of Water and Hazardous Materials
Environmental Protection Agency

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EPA REVIEW NOTICE
This EPA Report has been reviewed by the Office of Pesticide
Programs and approved for publication. Approval does not
signify that the contents necessarily reflect the views and
policies of the Environmental Protection Agency, or does
mention of trade names or commercial products constitute
endorsement or recommendation for use.

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EVALUATION OF THE POSSIBLE IMPACT OF
PESTICIDE LEGISLATION ON RESEARCH AND
DEVELOPMENT ACTIVITIES OF PESTICIDE MANUFACTURERS
By
Aldred E. Wechsler
Joan E. Harrison
John Neumeyer (Consultant)
For
Environmental Protection Agency
Office of Pesticide Programs
Robert E. O'Brien, Project Officer
EPA 540/9-75-018
February 1975

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PREFACE
This report was prepared by Arthur D. Little, Inc. (ADL)
Tinder Contract No. 68-01-2219 for the Office of Pesticide
Programs of the Environmental Protection Agency. The
principal authors were Alfred E. Wechsler, Joan E. Harrison,
and John Neumeyer (consultant to ADL). Other ADL staff
contributions to the program were: Joan B. Berkowitz,
Alan W. Burg, JohnT. Funkhouser, Janet M, Stevens, and
Edward S. Shanley. The authors acknowledge the guidance
and assistance of the EPA project officer Mr. Robert E. O'Brien
of the Office of Pesticide Programs. The study results were made
possible through the excellent cooperation and the information
provided by the National Agricultural Chemicals Association and
the following companies:
American Cyanamid Company
American Hoechst Corp.
Amchem Products, Inc.
Chemagro, Division of Baychem Corp.
Chevron Chemical Company
Diamond Shamrock Chemical Co.
E.I. duPont de Nemours and Company
Elanco Products Company
FMC Corporation
Gulf Oil Chemicals Company
IMC C orp.
Monsanto Chemical Products Company
Nor-Am Agricultural Products, Inc.
Nutrilite Products, Inc.
Occidental Chemical Company
Shell C hemic al C ompany
Stauffer Chemical Company (California and Connecticut)
Union C arbide C orporation
U.S. Borax Research Corporation
Velsicol Chemical Corporation
Zoecon Corporation
This report reflects the views of the authors and their inter-
pretation of those expressed by industry. It has not been reviewed
or commented on by other parties interested in pesticides such as
environmental groups, the U.S. Department of Agriculture, or
the staffs of academic institutions.

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TABLE OF CONTENTS
Page
I.	SUMMARY	1
A.	PURPOSE AND SCOPE	1
B.	APPROACH	1
C.	RESULTS	2
D.	CONCLUSIONS AND RECOMMENDATIONS	10
II.	INTRODUCTION	14
A.	BACKGROUND	14
B.	PROGRAM OBJECTIVES	15
C.	APPROACH	16
D.	REPORT ORGANIZATION	16
III.	TRENDS IN THE PESTICIDE INDUSTRY AND THE R&D PROCESS	18
A.	THE PESTICIDE INDUSTRY	18
B.	THE R&D PROCESS	28
C.	TRENDS IN R&D ACTIVITIES	34
D.	DECISION-MAKING IN PESTICIDE R&D	46
E.	TRENDS IN PRODUCT DEVELOPMENT AND INNOVATION	48
IV.	LEGISLATIVE ACTIONS AND THEIR IMPACT	53
A.	INTRODUCTION	53
B.	REVIEW AND COMPARISON OF FIFRA AND FEPCA	54
C.	SPECIFIC IMPACTS OF LEGISLATIVE AND REGULATORY ACTION 70
D.	GENERAL IMPACTS OF LEGISLATIVE AND REGULATORY	97
ACTIONS—RELATIONSHIP WITH OTHER TRENDS
E.	BENEFITS	112
V.	RECOMMENDATIONS TO REDUCE ADVERSE EFFECTS OF FEPCA	113
IMPLEMENTATION
VI.	CONCLUSIONS	117
Hi

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I. SUMMARY
A.	PURPOSE "AND SCOPE
Although the pesticide industry has developed under the constraints
and benefits of federal regulation for over 25 years, new pesticide
regulations promulgated under the Federal Environmental Pesticide Control
Act (FEPCA) of 1972 could have a significant impact on the innovative—
research and' development-—activities of pesticide manufacturers. Decreases
in innovation would ultimately affect the type and quantity of new pesticides
entering the market, would alter pesticide production and use patterns,
and could increase the cost of agricultural production. These effects
could be counteracted by potential improvements in safety and environmental
quality and by the development of new pest control methods brought about
in response to new regulations. **
The purpose of this program was to examine the probable effects of
past and current federal regulations on innovative research and develop-
ment (R&D) activity in the pesticide industry. More specifically our
goals were to:
•	Describe and identify trends in key factors that influence
innovative activity in the pesticide industry.
•	Examine the impacts of past pesticide legislation and
regulations on innovative activity in the pesticide
industry.
•	Assess the probable impact of recent pesticide legislation
on innovative activity in the pesticide industry and suggest
methods for minimizing adverse impacts.
Our work was focused on obtaining and examining industry's reactions to
past regulatory activities and industry's anticipation of how recent
and proposed regulations would impact future R&D activities.
B.	APPROACH
The trade, scientific and regulatory literature covering the
past 10 years was reviewed briefly in order to develop background informa-
tion on the research and development activities of the pesticide Industry.
Pesticide regulations from the Federal Insecticide, Fungicide and
Rodentlclde Act (FIFRA) of 1947 through FEPCA were examined and compared.
Discussions were held with the management, marketing, research, engineer-
ing and regulatory liaison staff of 22 companies representative of the
large and small, new and old sectors of the pesticide industry that
perform research and development. Information was obtained on the princi-
pal impacts of past regulations on R&D, the anticipated implementation
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of FEPCA and Its potential Impact on R&D, approaches to mitigating adverse
effects of FEPCA implementation, and trends in R&D activities that
demonstrated the impacts of regulations. This information, as well as
additional data obtained from EPA staff, the literature and trade associa-
tions, was analyzed and integrated into this report.
C. RESULTS
1. Structure and Market Factors
Among the many U.S. companies involved in the manufacture, formulation,
distribution, and sale of pesticides, the major innovative research and
development efforts are conducted by about 30 organizations that manu-
facture pest control products. Most of these companies are multi-product
firms, for which pesticides comprise less than 20% of the total sales.
About 2/3 of the companies engaged in pesticide R&D are large chemical-
or petroleum-based firms; several are multi-product pharmaceutical companies;
the remainder are a variety of smaller firms in which pesticides comprise
from 20% to 100% of all product activities. In many respects, the pesticide
industry and its R&D activities are similar to the pharmaceutical industry
and are characterized by:
•	A high degree of federal regulation;
•	Large R&D investments as a percent of sales revenues;
•	Significant risk, in product development, with large
expenditures on unsuccessful as well as successful
products;
•	Extensive product screening and testing programs;
•	Considerable time lag from invention to commercialization of
product; and
•	Competition among proprietary products of different companies.
The high risks associated with pesticide development are a result of
several factors. Only about one in 7000 potential products entering the
initial screening phase of R&D will result in a successfully marketed
product. Others are eliminated on the basis of efficacy, safety, cost,
competitiveness, or environmental factors. Because of the time lag
(presently 6 to 8 years) from invention to commercialization of pesticides,
additional risks are encountered because of the uncertainty of market
projections, commitment of capital for facilities, commitment for raw materials,
and the uncertainty of the registration process.
The highly specialized requirements for personnel (biologists,
entomologists, plant pathologists) for R&D facilities (analytical labora-
tories, greenhouses, experimental farms) and for pilot and production
facilities preclude shifts from pesticide R&D to R&D of other products.
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Since large sustained commitment of resources is needed, the principal
contributors to pesticide R&D are the multi-product firms with continuous
income from other products. There are few new corporate entries into
pesticide R&D, and there is continued management pressure to reevaluate
pesticides as products, based on risk and rate of return considerations.
Among the pesticide products, herbicides have experienced the largest
growth both in sales and In R&D; this trend is expected to continue.
Research and development in Insecticides has shifted from chlorinated
hydrocarbons to organophosphates, carbamates, and more recently juvenile
hormones. Directed research on fungicides is only modest because of the
lower overall market potential. Research on biological approaches to
pest control is also very limited.
Most pesticide R&D activities are focused on pests that attack major
crops—corn, cotton, soybeans, small grains, rice and alfalfa. Because
development costs for products for major crops are comparable to those
for minor crops, those products with lower potential sales volume are
naturally dropped.
Other market factors that affect pesticide R&D include: competition
and substltutabillty in the herbicide and insecticide market among similar
products for the same crops, foreign markets to supplement U. S. sales
and production activities, government agricultural support policies which
can either increase or decrease the demand for pesticides, AID and military
markets, pesticide demand, and the energy and petroleum shortages.
2. Trends in R&D Activities
The pesticide research and development process consists of:
•	Synthesis and screening—initial preparation of small
amounts of chemicals that are screened for pestlcidal
activity.
•	Preliminary data gathering—synthesis of larger amounts of
promising chemicals for use in laboratory or greenhouse
tests of toxicity, efficacy, and environmental effects.
•	Experimental field use—acquisition of use permits and
conduct of Intensive field studies on efficacy, applica-
tion rates and methods, residues, pathways and levels of
ecological penetration.
•	Registration—compilation of toxicity, efficacy, environ-
mental, and product data, submission to EPA, and obtaining
of a label.
•	Process development and marketing—engineering design
of process, pilot plant operation, plant construction,
and operation.
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The estimated cost for discovery and development of a pesticide is
currently about $7.5 million including the costs of unsuccessful compounds.
This cost has increased by over 100% since 1967, as a result of the grow-
ing sophistication of the industry, increased competition among products,
and the Increased costs of R&D, particularly the Increased field testing.
The costs of maintaining existing products has also increased. The cost
for developing a single successful product has increased from about
$1.0 million in 1960 to about $3.0 million in the early 1970*s. Much of
the R&D expenditures of pesticide companies, which average about 6% of
sales are devoted to obtaining data and information for registration of
new products and to the maintenance of the registrations of existing
products.
The timing of the R&D process, i.e., the duration from initial
synthesis to registration, hag increased from about 3 years in 1960 to
4.5 years in the late 60's and to more than 7.0 years at present.
Principal increases in timing have resulted from increased toxicity
(carcinogenicity, mutagenicity, etc.), residue, and environmental fate
tests, field tests, and the registration process itself. Similarly,
manpower levels for R&D in the pesticide industry have Increased by about
100% over the past 15 years as a result of toxicity, environmental and
field testing, and the requirements for constant attention to regulations.
Principal factors in decision-making concerning potential products
for continued R&D efforts include (in decreasing order of importance):
•	Efficacy—performance in solving a particular pest problem,
•	Cost in relation to existing or anticipated competitive
products,
•	Volume of potential market, and
•	Safety and environmental factors.
The number of new pesticide products developed annually by each
company has decreased by about 50% over the period from 1960 to 1970.
The decrease can be traced in part to regulatory requirements associated
with pesticide residues on food products. Caution by decision-makers in
a high-risk business, the decreased importance of minor use markets, and
the general decrease in innovative activity resulting from increased need
for defensive research on existing products have also contributed. The
number of product registrations per company has not decreased as signifi-
cantly, a trend indicating the need to register products for as many
applications as possible.
Other trends include an overall decrease in R&D on insecticides and
fungicides and an Increase in R&D on herbicides. In general, Industry does
not feel that biological control approaches are worth pursuing extensively
at this time because of efficacy, cost, market volume, and safety factors.
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In addition, technical difficulties in storage and stability, the lack
of patent protection, and anticipated problems in user acceptance have
also prevented investments in this R&D area.
3. Legislative Actions
The principal legislative actions that have affected pesticide
research and development in recent years have been FIFRA (1947), the
Delaney amendment to the Federal Food, Drug and Cosmetic Act (1962), the
policy changes in pesticide residue requirements during 1966-67, PR
Notice 70-15 (1970), FEPCA (1972) and the regulations proposed and promul-
gated under FEPCA since its enactment.
The data required for registration under FIFRA evolved from 1947 to
1971 at a slow,steady pace. The provisions that have had the greatest
Impact on pesticide R&D Include:
•	The data requirements for pesticide registration and labeling,
for example, toxicity tests and data including safety,
physical/chemical properties, efficacy, and labeling informa-
tion;
•	Data required for the establishment of tolerances on
agricultural commodities, e.g., chemical, toxicological
(acute, short-term, long-term), biochemical, reproduction
studies, etc.; and
•	The experimental use permit program, which required additional
data and permits for field testing of potential pesticide
products.
Significant step increases in the data requirements occurred as a
result of the Delaney Amendment, which prohibited the occurrence of any
known carcinogen in food products. Another step increase occurred as a
result of the policy changes of 1966-67, which required reevaluation and
rereglstration of pesticides that had been previously registered with
"no residue" or "negligible residue" status. These changes required
additional laboratory and field testing of already marketed (and newly
developed) pesticides in order to establish finite tolerance levels and
to ensure that carcinogens were not present in any residue. The PR 70-15
notice posed a number of questions pertaining to the fate and significance
of pesticides in the environment, questions for which extensive data had
to be obtained prior to registration.
FEPCA (also referred to as FIFRA, amended) contains many new provisions
and regulations that are now being implemented. Registration requirements
are similar to FIFRA, although pesticides in both inter- and intra-state
commerce are now covered by FEPCA. Major differences between FEPCA and
FIFRA Include:
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•	Additional data requirements to be provided with
registration;
•	Emphasis on demonstration that normal use of pesticides will
not result in unreasonable adverse effects on the
environment;
•	Strengthened suspension, cancellation and enforcement
procedures;
•	Classification of pesticides for general use or restricted
use;
•	Requirements for certified applicators for restricted use
pesticides;
•	Provisions for compensation for the use of others' test
data in support of registration applications;
•	Indemnity for certain persons suffering loss as a result
of suspension and cancellation of a registration;
•	The establishment of storage, disposal and packaging
provisions;
9 An expanded experimental use permit system with additional
data requirements;
•	Increased responsibilities and authorities for states
in regulation of sale or use of pesticides; and
•	Commitment to research to aid implementation of FEPCA.
Those provisions of FEPCA that are expected to have major impacts on
pesticide R&D are described further in the following report.
In parallel with these regulatory changes has been a shift in emphasis
in the registration process and data requirements from efficacy and safety
(when the regulations were administered by USDA and FDA) to safety and
environmetal effects (under the present administration by EPA). Industry
believes that this change in emphasis and accompanying attitude of the
regulators has had as much impact on R&D as the regulations themselves.
4. Specific Impacts of Legislative Actions
RegisOation requirements—The steadily increasing requirements for
data on health, safety, and environmental effects to support registration
of pesticides have significantly increased the cost and time frame for
pesticide registration and development by industry and have resulted in
a decrease in the rate of innovative research and development activity
as was discussed previously. These costs and delays have been balanced
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by a greater understanding of pesticide effects, derived from registration
data, and by the registration of effective, safe and environmentally sound
pesticides. The increase in cost and time frame for pesticide development
and registration result from both technical data requirements and procedur-
al requirements.
Industry generally accepts the fact that increased technical data are
needed to provide the scientific basis for registration of pesticide
products. Although there are some specific difficulties encountered in
test requirements and test procedures, industry is capable of meeting
technological requirements with the associated cost and time increases.
Procedural problems of pesticide registration, on the other hand, occupy
the concern of industry and are felt to result in unacceptable delays and
costs that discourage innovative activity. Industry feels that these
procedural problems coucd be resolved through conscientious efforts by
both the regulatory agency and industry. Other impacts of increasing
data requirements for registration include: earlier decision-making with
respect to pursuing specific potential products, specialization by pesticide
research organization in certain technical areas and use of contractor
assistance in others, and additional information on pesticide fate and
significance in the environment which may help prevent long-term adverse
environmental effects.
Experimental Use Permits—The proposed experimental use permit system
under FEPCA will increase the costs, timing, and risks in pesticide
research and development activities. Industry can be expected to challenge
the proposed regulations unless methods are found within the scope and
intent of the permit system to obtain data on efficacy, application rates,
environmental and geographic variables, and to obtain marketing informa-
tion such as acceptance by the farmer, comparison with competitive products,
etc. Because use permits were "easy to obtain" and because the data and
Information were developed for the decision-making process of pesticide
development on a timely and cost-effective basis, the looseness of the
regulations may have resulted in indiscretions and violations of the intent
of the permit system.
Changes in the experimental use permit system proposed under FEPCA,
such as the restriction on pesticide resale, limitations on exceptions
to the permit system, added data needed to obtain the use permit, and
procedural requirements are designed to prevent such indiscretions. These
changes have been labeled an "overreaction" by industry, which predict
that significant impacts on R&D will occur. Industry feels that restricting
marketing data from the field permit program may hamper the decision-making
process and result in the flow of fewer acceptable products to the market-
place.
Data needed to obtain experimental use permits will be required early
in the screening process. At that point in time, many potential products
have not been eliminated by screening; thus an increase in the cost of
R&D will result. Greater staffing to manage the field program and increased

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facilities (experimental farms) will also increase R&D costs. The duration
of the R&D process, from discovery to registration, may increase by up to
12 months. A shift in the order and scheduling of R&D activities may also
occur, so that more toxicological and environmental degradation work will
be required in early stages of product screening. Smaller pesticide companies
may be more severely affected than large companies. The overall impact of
the new experimental use permit system will decrease innovative activity
on new pesticides, encourage expansion of present product lines to more
applications, and result in increased R&D costs passed on to the consumer,
but will provide a better control of the environmental Impact from pesticide
use.
Restricted Use/Certified Applicators—The restricted use classifica-
tion system and the requirements for certified applicators will have
little or no direct impact on R&D activities because they do not require
additional data, research activities, additional R&D staff, or changes in
the time frame for R&D. Industry anticipates that large numbers of
applicators will be certified and that pesticide preferences and markets
will still be determined by product efficacy and cost rather than use
classification. Industry is uncertain as to whether the use classification/
certified applicator system will aid the registration of certain product*
for restricted use that might otherwise not be registered.
Compensation for Others' Data—Section 3(c)(1)(D) of FEPCA dealing
with compensation for the use of other companies' data in support of
registration was strongly supported by industry in the legislative formation of
FEPCA. This provision will probably provide administrative and procedural
problems for EPA and industry but will have little impact on research and
development activities.
Pesticide Reregistration—The reregistration of currently registered
pesticides* as required by FEPCA, will most likely decrease innovative
R&D activities by industry over the next 2-5-year period because of the
anticipated additional data requirements for reregistration. These require-
ments are expected to catalyze the removal of presently marginally profit-
able pesticides, particularly those for minor crop use, from the market.
Industry has given little attention to reregistration because of other
more pressing problems presented by FEPCA.
Other major changes in regulations resulting from FEPCA—indemnification
resulting from suspension and cancellation of pesticides, books and
records requirements, enforcement procedures, intrastate coverage,
pesticide disposal provisions, etc.—are expected to have little direct
impact on pesticide R&D and only secondary impact through marketing and
sales effects.
5. General Impacts of Regulatory Actions
The Increased costs of pesticide R&D, caused partly by regulations,
will probably result in an increased emphasis on short-term return on
R&D investment and a decreased emphasis on effort which can bring long-
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term, but relatively uncertain, return. Thus, there will be increased
effort to capitalize on existing products, extend product lines to new
applications, and conduct defensive research on existing products. This
defensive research will result in a decreased emphasis on new innovation
in pest control. The projected market value of a potential pesticide
product will have to be higher for the compound to be developed through
the more costly R&D process. Fewer new pesticides are expected to be
registered and enter the market, and potential products without a relatively
certain promise of return may be "placed on the shelf." More importance
will be given to international markets to bear the costs of the R&D
process.
Regulations have resulted in an extension of the duration of the R&D
process to about 7 or 8 years from initial synthesis to registration
of a new product. Within this time period, a reordering of parts of the
R&D process has occurred, so that needed environmental and toxicological
data for experimental permits or for better decision-making is obtained
as early as possible. The reordering of the R&D process also affects
decisions for new plant construction investments, as well as for market
development.
Staffing needs of companies engaged in pesticide R&D have increased;
more biologists, environmental chemists, engineers, and regulatory liaison
personnel are needed.
Industry has some concern over the decrease in available patent life
of proprietary products brought about by the increased duration of the
R&D process. However, there is more concern over the possible decrease
in market share and profitability resulting from the entrance of new
competitive proprietary products than over the loss of a year or more
of patent life. Some form of proprietary or patent protection is especially
needed in the area of biological controls to stimulate R&D activities in
this area.
Regulatory actions as well as general economic considerations will
decrease the number and availability of pesticides specific to minor crop
use. Once a major market is developed the use of pesticides will be ex-
tended to minor crops. However, little innovative research for pest
control on minor crops per se is expected to occur.
The impacts of regulatory actions—costs, timing and procedural
problems—can be better absorbed by the large diversified pesticide
companies than by the smaller companies involved in pesticide R&D. Thus,
although the climate and potential for innovative R&D may be better in the
smaller companies, the number of smaller companies conducting R&D will
probably decrease. Similarly, the number of new companies entering in
the pesticide R&D area will be small, because of the large arid long-term
commitment required before any new product can provide a reasonable return.
The impacts of regulations apply equally to biological controls as
to innovative chemical pesticides. These impacts, coupled with the
technical problems and limited present markets, suggest that R&D on biological
control will have to be supported or subsidized by the federal government before
any reasonable progress can be made in today's economic climate.
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P. CONCLUSIONS AND RECOMMENDATIONS
The major conclusions developed In this study axe:
1.	Over the past 25 years pesticide regulations have increased
slowly and steadily In breadth and depth; their impact on
innovative research and development in industry has increased
in parallel. Major impacts on R&D activities have already
occurred, prior to FEPCA as a result of the requirements for
safety and environmental data. Although the implementation
of FEPCA will result in additional impacts on specific portions
of the R&D process, the act itself does not represent drastic
changes in innovative activity.
2.	The principal impacts of this steady growth in regulatory
action on pesticide R&D activities include:
•	substantial increases in the time and costs of pesticide
development;
•	increased risk for the pesticide developer;
•	increased allocation of R&D resources to the defense and
maintenance of existing product lines and extension of
pesticides to new uses at the expense of decrease in
innovative R&D;
•	reordering of the timing of specific R&D activities and
reallocation of some R&D manpower resources;
•	increased emphasis on development of products for
foreign markets in order to increase sales volume.
3.	Implementation of the registration requirements and experimental
use permit system under FEPCA will result in increased R&D costs,
and lengthening and reordering of the R&D tasks. Only minor
Impacts on R&D activities are anticipated from FEPCA provisions
dealing with certified applicators, restricted use classification,
compensation for data, packaging, disposal, etc.
4.	The principal impacts of pesticide regulations on future
pesticide product development are:
•	continued development of potentially high volume/profit
compounds such as herbicides;
•	continued emphasis on products for major agricultural
crops with decreasing emphasis on products for minor crops; and
•	continued decrease in the number of new pesticides
which enter the marketplace.
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5.	The principal decision-making factors in the development of a
potential pesticide product are, in order of importance:
•	efficacy,
•	projected cost compared with competitive products,
•	anticipated sales volume and profitability,
•	human safety (toxicity), and
•	environmental impact.
Recent regulations may eventually increase the importance of
environmental impact as a decision-making factor; the other
factors remain more important in determining whether potential
products will reach the marketplace.
6.	The large, established, multi-product, diversified pesticide
developers will continue to be the major source of R&D in
industry since they can continue to develop and market new
products, given the required time and cost investments necessary.
The smaller and more recently formed companies may not be able
to sustain the increases in R&D costs and extended product
development time. They will either withdraw from the R&D function,
be consolidated with larger companies, or withdraw from the
marketplace. This will result in a decrease in innovative
activity, due to the decrease in the number of companies partici-
pating in pesticide R&D.
7.	Potential products based on most biological control approaches
have serious technical problems, are not cost competitive, have
poor anticipated acceptance by the user, and are not believed
by industry to be more safe than chemical approaches. Biological
controls are not expected to gain a significant market share in
the near future despite the encouragement provided in recent
regulations.
8.	Industry has recommended ways to reduce some of the anticipated
adverse impacts of FGPCA; most of these address procedural
changes that will help reduce the cost and duration of the
pesticide development and registration processes. Improvement
of the long and inefficient registration process by EPA will
remove a significant barrier to pesticide development and use.
However, these procedural and registration changes, by themselves,
will not significantly increase innovative pesticide research
and development. Federally supported Incentive programs which
also eliminate other significant barriers are needed to promote
Innovative pesticide R&D and Increase the number of new
pesticides that are safe, effective and environmentally accept-
able.
Principal recommendations for reducing adverse effects of regulatory
action on pesticide R&D are:
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1.	Develop policies and procedures for improving the pesticide
registration/review process at EPA:
•	publish complete registration guidelines with a balance between
flexibility for different pest control approaches and specificity
of detailed data requirements for all approaches;
•	develop procedures for updating registration guidelines;
•	establish definitive schedules for the registration/review
process with attention given to frequent EPA/registrant
communication;
•	incorporate seasonal effects of field tests and pesticide
usage in the timing of registration reviews; and
•	develop procedures for consistency of internal review at EPA.
2.	Develop policies and procedures for expanding and diversifying the
EPA pesticide registration staff:
•	recruit staff experienced in agriculture, pest control
development, health and safety, environmental effects at
increased pay levels;
•	develop programs for internship/work/study of EPA registration
staff at USDA, universities and industry or develop an EPA/
university/industry exchange program;
•	provide for flexibility in number and experience of registra-
tion staff for peak load periods, including seasonal trends
in experimental permit applications.
3.	Develop policies and proceduresfor improving intra- and inter-
agency communication, liaison and cooperation with EPA Criteria and
Evaluation Division and Registration Division, EPA regional offices,
USDA staff, state environmental and health agencies, and agri-
cultural extension services,
4.	Develop policies and procedures to enhance the implementation and
benefits of the experimental use permit programs: for example,
a co-monitor program for evaluation of field studies by EPA
Registration Division or EPA regional staff* allow distributors
and dealers to participate is Che experimental use program.
5.	Conduct research and communicate the results to industry in the
following areas:
•	cost/benefit analyses on the decision-making factors and criteria
for acceptance of toxicity and environmental Impact data for
pesticide product registration, suspension, and cancellation;
•	biochemical studies to elucidate mechanisms of pest control and
enhance new pest control approaches;
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•	biological control approaches—mechanisms of action, stabiliza-
tion of viruses and bacteria, application methods, and consumer
acceptance;
•	pesticides specific to minor crop uses;
•	toxicology and environmental information on classes of chemical
and biological pesticides In common use or expected to be
developed.
6. Develop a broad program of incentives to foster innovative R&D
activities by industry and universities. The incentives considered
should include: government-funded research, government-performed
research, proprietary protection alternatives, insurance incentives,
R&D loan/payback systems, total integrated pest control systems,
etc.
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II. INTRODUCTION
A. BACKGROUND
During the past quarter century of intensive organic chemical pesticide
development, many products and product forms have been placed on the market.
These include all types of chemicals, the principal varieties being insecti-
cides, fungicides, herbicides, plant growth regulators and some biological
products. Modern food production and public health programs are dependent
upon the use of these pest control agents. The number of people who use
pesticides is increasing continuously; the number exposed to the effects of
these chemicals is almost the total population. The production and use of
pesticides in the United States continues to grow in response to the demands
of the U. S. and foreign users. Production of some pesticides are reaching
new levels, while others are being severely limited because of the substitu-
tion of new or improved chemicals or changes in U. S. and foreign markets.
At the same time, concern for environmental quality has led to legislative
action which may affect the present research, and development, production
and use of pesticides.
The development cost for a new pesticide is influenced by a number of
factors. Some are related to the nature of the chemistry of the pesticide
and involve the inherent risk in developing a specific chemical ingredient
with desired characteristics. In the past the most important influences
on costs were those caused by the nature of our economy, i.e., labor, equip-
ment, sales costs, facilities, overhead, etc., as well as the intended use
of the new pesticide ifor food crop or non-food crop). Pesticide manufactur-
ers have been aware of the high risks and costs involved in the development
of a new pesticide. Another important part of each decision to develop a
new pesticide is the anticipated competitive situation in the marketplace.
A new compound which has better activity, is safer, more convenient to use
or less costly than competitive pesticides has economic advantages which
make it attractive to the market. These factors are often unknown or
difficult to determine in the early stages of product development. If
adequate technical support is to be given to new product development, there
must be sufficient return to finance such support over at least the initial
years of consumer use while correct usage is being learned. Industry makes
its business decisions as best as possible on market-oriented bases, on
knowledge of the trends in the foreign and domestic marketplace, and in
anticipation of environmental requirements and potential restrictions.
The pesticide chemical R&D process is long and involved. In contrast
to many chemicals which move rapidly from initial development to use in
products, it is often four to five years after development and registra-
tion before the new pesticide chemical will show valid signs of real
profitability. Thus, decisions are often made on the basis of limited
knowledge of the true potential of the new pesticide and the effort required
in its development and marketing. When faced with the decisions regarding
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the commitment of large R&D expenditures to develop a new pesticide,
management must look to the anticipated profitability of the market for
the compound, and compare it with the potential return on investment for
the development of other chemical products.
The pesticide industry has developed under the constraints and bene-
fits of federal regulation for over 25 years. The possible impact of new
pesticide regulations on the innovative activity of pesticide manufacturers,
particularly research and development, could be serious for manufacturers,
agriculture and the public. Restrictions on use, threat of suspension or
cancellation, Increases in data requirements, timing, and costs of the
registration process could lead to a decrease in innovative activity in
the pesticide industry. Such actions could decrease profitability and
increase the cost of innovation within the pesticide industry, create a
management climate leading to the reallocation of resources and commitments
from pesticides to other research pursuits, and increase the risks associ-
ated with innovative research. Decreases in innovative activity will
ultimately affect the type and quantity of new pesticide products entering
the market, alter pesticide production and use patterns, and could result
in increased cost of agricultural production. Countering these effects
are the potential improvements in human safety and environmental quality,
and the development of new pest control techniques brought about in response
to new regulatory actions.
The probable effects of past and current regulatory action on innovative
research and development activity in the pesticide industry is the subject
of this report.
B. PROGRAM OBJECTIVES
The principal objectives of this program were to:
(1) Describe and identify trends in key factors that influence
innovative activity in the pesticide industry, e.g.,
characteristics of the industry, research and development
staff, approaches, and costs, characteristics of the
market, etc.;
C2) Examine the impacts of past federal pesticide legislation
and regulations on innovative activity in the pesticide
industry; and
(3) Assess the probable impact of current federal pesticide
legislation on innovative activity and suggest methods
for minimizing adverse impacts.
Emphasis was placed on studying those market or structural factors
which were most relevant to Innovative (research and development) activities.
The work focused on obtaining and examining industry's reaction to past
federal regulatory activities and industry's anticipation of how current
and proposed federal regulations would impact future research and develop*
ment activities.
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This report reflects the views of the authors and their interpretation
of the views expressed by industry. It has not been reviewed or commented
upon by other parties interested in pesticides such as environmental groups,
the USDA, or the staffs of academic institutions.
C.	APPROACH
A brief review of trade, scientific and regulatory literature covering
the past ten years was conducted in order to: (1) describe the R&D process
in the pesticide industry; (2) identify companies with pesticide research
and development activities; (3) obtain valid sources of necessary market
and sales information; and (4) obtain published views of the impact of
regulations of innovative activity. Pesticide laws and regulations from
the Federal Insecticide, Fungicide and Rodenticide Act of 1947 (FIFRA)
to the Federal Environmental Pesticide Control Act (FEPCA, or FIFRA amended)
were examined and compared. A series of scenarios depicting possible imple-
mentation strategies for FEPCA and resultant potential impacts on innovative
activities were prepared. Companies with major pesticide research and
development activities were identified, And discussions were held with 22
companies representing large and small, established and newly formed
segments of the pesticide industry. The discussions involved personnel from
management, marketing, financial, research, engineering, regulatory liaison
and legal staffs of the industry. The discussions focused on: (1) the
principal impacts of past regulations on R&D activities; (2) the anticipated
implementation of FEPCA and its potential effects on R&D activities; (3)
recommendations for mitigating any adverse effects of FEPCA implementation;
and (4) data which demonstrated trends in research and development and
Impacts of regulations. Our reception at industry was excellent; discussions
were open and frank. This was made possible in part by industry's desire
to provide some "feedback" to EPA through an independent party and by our
agreement not to directly associate specific comments, data or information
with any particular company or product. Even with this agreement, some
companies were reluctant to provide us factual data on costs, profits,
markets, research timing or staffing. In our discussions and data collec-
tion at industry, we attempted not to duplicate the forthcoming National
Agricultural Chemical Association (NACA) survey (an update of the 1970
survey) nor to duplicate information that was prepared by industry in res-
ponse to publication of proposed regulations. We also discussed the imple-
mentation of the current regulations with NACA staff and EPA registration
staff. The notes, comments and data obtained in these discussions were
examined, analyzed and integrated into this report.
D.	REPORT ORGANIZATION
Section III presents a brief background description of the pesticide
Industry, focusing on research and development activities. The pesticide
research process is described, and trends in R&D staffing, expenditures,
time frame, and outputs are presented. Section IV summarizes and compares
the major regulatory actions from 1947—FIFRA—to 1972—FEPCA. A discussion
of the possible specific impacts of FEPCA and its regulations is next pre-
sented, followed by a discussion of more general impacts of the regulations
and other factors on R&D activities in industry. Topics may be discussed
in more than one of these sections since they may represent trends in
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Industry as well as Impacts of both past legislation and FEPCA. Section
V presents industry's and ADL's recommendations to minimize the Impact of
FEPCA on R&D and to encourage innovative research. Finally, the major
study conclusions are given.
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III. TRENDS IN THE PESTICIDE INDUSTRY AND THE R&D PROCESS
A. THE PESTICIDE INDUSTRY
In 1971 the U. S. Tariff Commission reported that 87 companies pro-
duced basic pesticides. Only a few can be considered "pesticide companies,"
i.e., companies which concentrate almost all of their effort on pesticides.
Most are multi-product companies which produce a variety of chemicals.
Some concentrate heavily on agricultural products (40-100% total business)
while others rely on agricultural products for less than 15% of their
business. Most of the companies which contribute significantly to pesti-
cide R&D are in this latter category.
Figure 1 shows the channels of development, production, formulation,
and distribution of pesticides. In most cases, two or more functions are
assumed by the same company. For example, a company may develop and
formulate its own product, relying on some basic chemical producer to
manufacture the active chemical. In other cases, a developer will license
a chemical to a company which will both produce and formulate the product.
Other combinations are common. In the recent past there has been a small
trend towards vertical integration, i.e., a company carrying a product
from development to retailer. This circumvention of distributor is a
relatively new occurrence and has not been notably successful.
Companies can enter the pesticide business by assuming any of the
roles mentioned above, although not necessarily with ease. To enter the
manufacturing or R&D phase, companies can:
1.	License potential chemicals or purchase the patent rights
of pesticldal chemicals developed by other companies.
2.	Manufacture non-proprietary chemicals if a competitive
edge can be gained in marketing or by an improved manu-
facturing process.
3.	Purchase small companies already Involved in pesticide
development or manufacturing or both.
4.	"Start from scratch" with the development and manufactur-
ing of proprietary compounds.
5.	Expand and diversity existing, related activities to
include pesticide development and manufacturing.
Companies generally either make a large initial investment with the
laboratory equipment, farm facilities and highly qualified professionals
representing several disciplines; or make a small initial investment,
giving a few professionals some lab space and allowing them to "see if
they can come up with something." Many of the firms that have conducted
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Imports
~ Exports
Imports
Exports
Developer
Formulator
Producer
(Manuf ac tur er )
Non-Proprietary
Compound
Retailer
(Dealer, Local Coopera-
tives, Applicators)
Distributor
(Wholesalers, Brokers,
Manufacturer Branches,
Agents, Regional
Cooperatives)	
Consumers
(Farmers, Applicators, Institutional
Users, State and Federal Government,
Home Garden and Commercial Users)
FIGURE 1. CHANNELS OF PESTICIDE DEVELOPMENT AND SALE
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research and development for 10 to 20 or more years started by this
latter method, the "Edisonian" approach, while more recent entrants have
either made a large investment of manpower, etc., or have purchased another
company. Most companies involved in pesticide R&D indicate that a large
initial investment is necessary in today's competitive market. The
recommended minimum for entering the pesticide business (starting from
scratch) is:
•	$7 million to develop the first pesticide and a total of
$50 million to commercialize the first successful product
to the point of obtaining significant return on investment.
•	10 years of "dry time" until a return is seen on the
investment. This includes discovery, testing, registra-
tion, plant construction, and initial marketing efforts.
The magnitude of this initial effort limits the type and size of
organizations which can enter pesticide research and development. In
most cases, only larger firms can risk this amount of money with no return
on their investment for ten years. One company we contacted referred to
pesticide R&D as a "poker game," with only the larger firms able to ribk
the initial ante. Larger firms also have other product lines which can
support the "dry times" both in developing initial compounds and in the
continuing development of further compounds. Some of the companies now
conducting R&D initially purchased patent rights or licensed pesticidal
compounds to provide the continuing income necessary to get over these
times.
Currently there are about 30 companies which contribute to innovative
research and development in pesticides in the U. S. Most of these are
multi-product firms for which pesticides comprise less than 20%, and in
some cases less than 1%, of their total sales. About 70% of the companies
which contribute to pesticide research and development are large basic
chemical companies, including the major oil companies. Large multi-
product pharmaceutical companies comprise another 10% of the firms which
conduct pesticide research and development. The final 20% is comprised
of a wide variety of smaller firms. Pesticide sales in these smaller
firms can make up anywhere from 20-100% of total sales.
The multi-product companies have a common basis in their starting
points for R&D, both In terms of developing products and initial entry
into the business. They all have active synthesis activities which
make large numbers of organic compounds available for screening. The
major chemical companies screen 5,000-10,000 compounds for pesticide
activity per successful product.' The compounds may be chosen at random
from synthesis activities in other product lines, or they may be synthesized
by structural modification of a known class of pesticides. Historically,
the empirical method of random screening has been the most widely used
approach to pesticide research although all companies now combine this
approach with the more directed method for discovery which relies on
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prediction of biological activity and synthesis of appropriate compounds
based on the knowledge of the crop and pest. It appears that the use of
the directed synthesis approach, which involves less risk and cost, will
continue to increase with the gradual accumulation of fundamental bio-
chemical knowledge.
Since most of the companies which conduct pesticide R&D are multi-
product by nature, it is useful to compare the relative attractiveness
of the pesticide product line with other chemical and pharmaceutical
activities. Within large firms the various product divisions compete for
research money as distributed by management, and there is an ever present
possibility that management will decide to rechannel pesticide efforts
Into other product lines. Some of the factors which contribute to decisions
to stay In or to get out of the pesticide business are the following.
Rate of return and profitability—As mentioned earlier, there is an
initial "dry time" of up to ten years before a company which has just
entered the pesticide R&D area can expect to commercialize a product (unless
they have bought an existing pesticide firm or have unusual luck). Once
a company has become established in the pesticide area the average time
before obtaining the return on investment made for a specific potential
product averages about 8 years. Managecs in the pesti_ide divisions of
these large firms are often concerned that this time period exceeds the
"half-life" of the average decision maker in top management, and that
products involving less time for return, e.g., plastics with a four-year
development time, might be favored for that reason. Turnover in management
seems to be a problem in those large firms which have not yet developed
their first successful compound.
For individual products the rate of return and profitability after
commercialization of a product varies considerably. Rates of return as
low as 25-30% are acceptable to sane companies if an $8-10 million market
is assured. For a $3-4 million market, a minimum of 40% rate of return
is acceptable. Profitability, of course, is also a factor. For some
companies a 10% profitability is necessary with a market of $100 million
gross sales. Other companies generally expect 25-30% profitability.
The percent profitability generally depends on the relation of the total
expected sales volume to the minimum sales required to contribute signifi-
cantly to company profits and to make up for development effort spent on
products which never could be marketed successfully. Pesticides, in
general, are lower in profit but higher in total sales than other specialty
chemical products such as pharmaceuticals.
Companies involved in pesticide R&D have increasingly turned toward
higher profitability pesticides, i.e., herbicides, which in most cases
are more profitable than insecticides. Some companies are becoming
increasingly concerned about delays in getting a product out on a market
because the price that consumers are willing to pay and thus the profit-
ability of the product often depends on its newness to the field.
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1. Risks in the Development Process
Generally, random screening of compounds in pesticide research yields
a success to failure ratio of 1 to 7,000 (the lowest reported in our
discussions with industry was 1:5,000, the highest, 1:20,000). Not all
failures are eliminated early in .the research process. One company stated
that: the investment needed to find out whether a pesticide was going to
be viable (both from the marketing and registration point of view) comprised
about 50 to 60% of the entire cost of development, and that this invest-
ment has increased from about 30% in 1968. The timing of the decision on
whether a compound is viable varies widely with the company, but for most
it involves at least two screening processes. Most companies indicate
that the difficulty in making market projections so far in advance (because
of the long registration process) compounds the risk involved in a "go-
ahead" decision on a pesticide product. Some companies plan to make that
decision within the first two years of the development of a pesticide so
that they can obtain commitments from raw material suppliers. Therefore,
the companies have to anticipate market factors 6-8 years in advance.
Thus, the development of pesticides often involves more risks than the
development of many other products. The risk presented by investment in
product facilities, although large, is no greater than that of other
product lines in other industries.
Although the risk and time required for a return on investment would
seem to make other product lines more attractive, the fact that there are
a large number of multi-product firms involved in pesticide R&D indicates
that other factors such as volume, sales and profitability may counteract
these negative factors. The risk, and "dry time" seem to become more
important, however, if the company is just getting into the business and
does not yet have products on the market to support the ongoing research
efforts. This is the time when pesticide R&D efforts are especially
susceptible to management "cold feet" or lack of "patient money."
The adaptability of the pesticide R&D investment to conversion to
other product lines is determined by several factors:
•	Manpower—the large numbers of organic chemists and
technicians required for synthesis and process development
are substitutable. However, the specialized plant:pathologists,
biochemists, entomogolists, and other crop and pest specialists
cannot be transferred to other product lines. This is confirmed
by reports of companies "getting out of the business" attempt-
ing to help their more specialized staff obtain jobs in other
companies which are continuing their pesticide R&D work.
•	Facilities—With increasing sophistication in environmental
testing and the need to cut down on delays, companies are
required to invest in more specialized expensive equipment
in the overall pesticide development process. This equipment
and screening facilities, such as insect labs and greenhouses,
are not substitutable. Farmland for field testing is easily
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reverted to capital.
•	Production—The largest investment in developing a pesticide
product line is the capital needed for the plant that will
produce the product. This represents an investment of up to
$30 million in many cases. This plant may or may not be
adaptable for other uses. Some of the equipment may be used
for other chemical processes, but there are likely to be
particular processes required by the production of the pesticide
which necessitates the use of specialized equipment. It is
often difficult to find other uses for this specialized, and
often expensive, equipment. If it is possible to use the plant
for other products, it usually does not yield the most cost
effective process for this other production.
•	The stage of development of a pesticide line—If a company decides
to drop out of the business before it has gone into production
of a salable chemical, the transition can be made with a capital
loss of about $1-10 million depending on the amount of equipment,
tests, manpower acquired, and whether a pilot plant was built for
production of the chemical for experimental use.
Companies that have been successful in the pesticide R&D area and
have developed a diversity of successful products reported to us that
they would go into pesticide R&D area again if presented with the
opportunity today.
Companies that have been only moderately successful stated in our
discussions they would either decide Immediately that the risk was too
high or drop out during the long wait for return on their investment.
The small investment and Edisonian approach to research is no longer
possible today. The initial investment of past years did not involve
the facilities and manpower which are necessaty today for environmental
and safety tests which are part of pesticide development. The increases
in the development costs came slowly to companies that were able to use
this approach and were supported by pesticide products which were already
on the market. New companies however have to make an initial investment
'Which reflects the increased development costs.
The resultant trends are:
1.	Multi-product firms already in the pesticide business will
continue to be the main contributors to pesticide R&D since
they have the income to provide continuous support to the
investment requirements of pesticide development.
2.	Most of the pesticide R&D will continue to be done by a
combination of random screening of compounds synthesized for a
variety of efforts and screening of compounds specifically
synthesized for pesticidal activity. This latter method will
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continue to grow in Importance.
3.	While a few new companies will enter the pesticide R&D area,
there will be a general consolidation of pesticide R&D companies
centering around companies that have a well established pesticide
product line and can support the continued development of new
pesticides.
4.	If risk and rate of return stay at present levels, pesticides
will continue to compete effectively for R&D dollars within
multi-product firms.
2. Trends in Pesticide Products
Herbicides—In the mid-sixties a few new herbicides became spectacular
successes as profitable compounds because they were timely in filling the
need to Increase manpower productivity and yields. As a result many
companies placed increased emphasis on herbicidal screening which has led
to a rapid increase in the number of herbicides on the market. Many of
these products are closely related based on similar chemical structures
indicating; a rapid synthesis of related compounds by industry based on the
initial successful herbicides.
Insecticides—Currently less R&D is being done in the insecticide
area than in the herbicide area because of the general lower profitability
of insecticides. Research has moved away from chlorinated hydrocarbons
because of their persistence and other environmental problems. Many
organophosphates came onto the market In the early fifties and they continue
to be a focus of research. Carbamates have developed more recently and
have begun to assume a significant role in the ihdustry. Much of the
innovation in the insecticide area is coming from basic research and a
better understanding of the comparative insect and mammalian enzyme
systems. The search for insecticidal compounds is directed toward dis-
rupting particular enzyme reactions that became known through this basic
research. In a similar way, hormone systems have come into focus for
pesticide R&D. For example, as the stages of growth of particular insects
are understood, chemical analogs of the hormones which trigger these
stages of growth can be synthesized and used to disrupt growth patterns.
Juvenile hormones act in this way preventing Insects from reaching the
reproduction stage.
Juvenile hormones and most pheromones are not viewed by industry as
biological controls since they are chemicals, which act in the same way
as other chemical controls, i.e.', by disrupting the normal chemical reactions
of the insect. Those that are considered to be biological controls are
general bacteria and viruses. Thus, there are three major categories
of insect control methods:
(1) . Synthetic organic and inorganic chemicals which
act as toxicants to the organism;
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(2)	Synthetic organic chemicals which are analogs or naturally
occurring insect chemicals and which disrupt a particular
stage of growth or reproduction; and
(3)	Naturally occurring pesticide compounds, e.g., bacteria and
viruses, which are selectively toxic to particular insects or
other pests.
Generally, there has been a continuing predominance of type (1) compounds
since this is the natural outcome of the empirical approach to research,
i.e., the screening of a wide variety of compounds. There has been a
very slow increase in type (2) compounds but they do not as yet comprise
a significant part of the market, nor has their utility as a means of
insect control been firmly established. Some companies are finding them
to be too specific in nature, i.e., the target pest does not comprise a
potentially large enough market to justify the development costs.
Bacteria and viruses have received attention from only a smaller number
of companies (about five), and some of these are curtailing their efforts
in this field. The reasons for this will be discussed later.
Fungicides—High value fruit and vegetable crops, for which high
quality is a necessity for sale, are the primary markets for fungicides.
The market comprised by the high-value fruits and vegetables is near to
being saturated since there is little room to increase usage per acre,
and acreage increases in these crops will be minimal in the future. There-
fore very little directed research will focus on fungicides, although,
as one company we interviewed stated, "if one was found in their regular
screening process that could be developed and made cheaply, they would
proceed with it."
3. Trends in Minor and Major Use Pesticides
As stated in the discussion on insecticides, some companies find that
the compounds which are designed to be specific (narrow as opposed to
broad spectrum) are often too specific, that is, the particular pest does
not comprise a large enough market to justify the development cost. With
increasing emphasis placed on the companies to develop specific pesticides,
companies are directing their efforts toward the major markets. Among
the larger companies which demand a larger volume of sales, the major
markets are comprised by: corn, cotton, soybeans, small grains, rice,
alfalfa. (Rice is included as a major market by thpse companies with
foreign as well as domestic markets.) Some of these companies have begun
eliminating, early in the screening process, compounds which do not show
promise in one of these major miarkets. Some of the smaller companies
(<$500 million net sales) consider citrus fruits, apples and some other
fruits to be major markets. The definition of major market depends on
the sales volume required to meet development and overhead costs as well
as to contribute significantly to company profit. Currently, about half
of the products on the market were developed for minor uses, for example,
strawberries, cumquats, etc. New products for these markets may only be
developed if they constitute additional uses for compounds developed for
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major markets. Additionally, some of the products currently registered
for minor uses may be eliminated if their sales volumes cannot justify
the costs of reregistration. The major and minor uses will be discussed
in more detail later; here they are mentioned as trends in product
development.
4. Trends in Market Factors
Competition and substitutability—In both the herbicide and
insecticide market there is much competition between producers. In the
herbicide market, for example, Amchem competes with Elanco for the soybean
market; both Ainiben and Treflan are used for pre-emergence weed control.
Shell competes with Elanco in the cotton market and with both Elanco and
Amchem for the soybean market. In the insecticide area, competition
exists among Shell, Velsicol, Chemagro, American Cynamid, and Hercules,
all of which produce products for use on cotton foliage. Chemagro and
American Cynamid also supply systematic products for use on cotton.
Most companies state that the existence of one or more products that
already occupy a market niche does not stop them from developing compounds
for that use. In fact, the companies feel it necessary to develop new—
but better—products for the same use even if it involves competing with
their own products since they are aware that other companies will be
pursuing the same use with new products. Industry predicts that the
competition will increase in products which involve major uses (cotton,
soybeans, etc.).
Competitive products are never entirely "substitutable" since they
involve differing efficacies and environmental and safety factors. However
many products are substitutable to the point that they help eliminate
the same pest organism. Sometimes a producer which has a commanding
share of a particular market will offer several products which can be
alternated to avoid build up of a single residue in the soil and to avoid
resistance. Farmers may change products on their own to prevent this
from happening.
Foreign vs. domestic markets—U. S. producers contribute significantly
in the world market with Canada and Latin America being the most important
export market. The market in Europe is increasing rapidly. Pesticide
exports will continue to grow, but other countries are increasing their
pesticide production capacity. Japan, for instance, is becoming a large
exporter of pesticides, although it continues to serve as a market for
American pesticides.* Several American manufacturers are beginning
to become more involved in foreign product ventures, including American
Cyanamid in Italy, Hercules in Central America, Velsicol in Mexico, and
Rohm and Haas, Dow, Rorer-Amchem and others in Japan.
Source: Trask, Harry A., U. S. Pesticide Industry 1967-1972,
Arthur D. Little, Inc. Service to Management Report, 1968, p 13.
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There has been an Increasing tendency for companies based in the
U. S. to turn to foreign markets to supplement domestic sales. It is
easier to obtain registrations in some other countries, since companies
which have only domestic plants generally wait to see whether they obtain
registration in the U. S., in order to know when and how large a plant
to build.
Government action—Government support programs generally increase
pesticide use. When farmers are guaranteed a support price for crops
under these programs, they tend to use more pesticides in order to grow
them more economically. For example, if government programs are based on
acreage controls, farmers tend to utilize more pesticides in order to
increase production per acre. If programs are based on production controls,
farmers tend to utilize more pesticides in order to minimize the acreage
and thus the cost needed to produce their allotted quantities.
AID programs have influenced the amount of herbicides and insecticides
exported. As countries Increase their food production it is unlikely
that they can increase pesticide facilities fast enough to cause a
significant decrease in pesticides exported in the AID program. Lately
AID programs have promoted increased exports of corn and soybeans to help
build up animal industries. These crops are large users of herbicides
and therefore an increase in production of these herbicides may be
expected.
Military Use—The use of defoliants in South Vietnam significantly
increased the production of 2,4,-D and 2,4,5-T, Tordon and organic
arsenicals. The end to a significant portion of this demand has resulted
in some of the companies, which relied on this production, to consider
withdrawal from this market.
Demand—The continued increase in volume of sales despite sharp
increases in the prices of many pesticides within the last year indicates
a continued increase in demand. Most of this is due to an increase in
domestic agricultural production in the last two years. Foreign demand
has not risen so sharply. Part of the price increase is due to increased
prices of raw materials. Additionally, over the years there has been an
Increased willingness on the part of the farmer to take extra precautions.
As food prices rise, the farmers may be willing to spend additional money
on fertilizers, improved varieties of seeds, causing additional expenditures
for pesticides to be made to protect these investments. In the past year
there has been a shortage of pesticides as a result of petroleum (raw
material) shortages, so that farmers have not always been able to meet
their requirements.
The demand for herbicides has increased, for instance, because
farmers have become more aware of crop losses represented by weeds making
use of the large amounts of fertilizers applied for the crop. Increased
demand for herbicides also reflects the decreasing supply and resulting
higher cost of farm labor. Farmers have traditionally combatted weeds
with mechanical or hand labor but now they are willing to spend more for
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chemicals to do the same jobs.
The elasticity of demand differs for Individual pesticides and for
pesticides as a whole. The demand for pesticides as a whole is relatively
Inelastic, that is, price fluctuations in pesticides do not affect the
total demand which is controlled more extensively by other factors such
as cost effectiveness, value of the crop, the seasonal nature of a particular
Infestation, and the weather. Among individual major crops, however, the
competition among products which eliminate the same pest is high, and
the elasticity of demand is high. For instance, if a product patent
life runs out and the price is cut by "me-too" firms, it is likely that
a particular compound will experience a significant increase In demand.
Minor crops, on the other hand, may present a very inelastic demand because
of the lack of more than one product to deal with particular pests.
B. THE R&D PROCESS
The discovery and development of a pesticide chemical is divided into
the following stages: synthesis and preliminary biological screening,
secondary biological evaluation, and small plot field testing; obtaining
an experimental use permit; large scale field testing, environmental
analysis, and toxicity tests; and full registration. Figure 2 shows the
timing of the various stages within the R&D process. The data do not
represent the development of any existing compound or the particular
process followed by any one company. It is intended to show the relative
duration and placement of the various efforts within the R&D process.
1. Synthesis and Screening
This initial stage is designed to identify compounds which show
biological activity and could be used to control some pest organism. As
described previously, most companies have a dual approach to the synthesis/
screening process. On one hand, there is the "shotgun" approach in which
compounds from non-pesticide related activities are randomly screened.
These compounds can came from other parts of the same company or from
other companies through agreements. The chances of discovering pesticldal
activity by this shotgun method is low, about 1 in 30,000. Most companies
which rely on this method have a large number of compounds which are
synthesized for other uses, e.g., pharmaceuticals. Some smaller companies
will purchase compounds which are rejected by multi-product companies
and screen them for pesticldal activity.
The second approach to synthesis/screening is the Mrifle" approach
which focuses on functional groups known to have pesticldal activity.
Compounds are synthesized by chemists, which number about 5 to 10 persons
in many companies. The focus of their synthesis comes from the known
functional groups and from modes of action in pest control which are
identified by entomologists and plant physiologists on the staff. This
approach to synthesis generally yields a much higher percentage of success-
ful products. The more "hungry" a company is for new compounds, i.e.,
28
/

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S.MtaK
Je-ewwfcs
himrY Sc'WIvm
I 6 BlfMrti
Secondary and Tertiary Screening
1 »-12W«ekt
Continuing Low Level Marketing and Proem Oewiopment Work
D«m<«n Poun, EtaWatmn of "L—d»"
PreHrraaery Laboratory DM* CllMiia9
IS-36Wwks (initial Toxeity. Preliminary Proce*Wwkl
A Oecston Mnt. Elimination of "hon-eompetitMe Cost" Compound*
Early Synthesis
20 Week* (Synthetic ofMl Amounts of Commmdl
Small Plot Field Teat: EHicacy and Soma Residue
12 Months
U&-
Point. Bsed on Efficacy, on Whether or Not to
Two-Yaer Toucotogy Tern (Includes AH Tonicity Tests)
Approval
Experimental Permit
4 7 Months
Finieh
_L—
|4ddiiiOiel_|
Tests at needed
Large Scale Field Tettinq (3-Seaaon)
EfMHomncnt»l Laboratory Tettinq
^ 12-18 Months
Prepve A point ton
J 4 Months
Receivi
CPA BWa. of Reo«.r«,on Aoo^.on
L_ _		
'	Testj as Needed
Plant Construction and Comnvri
29
FIGURE 2 REPRESENTATIVE TIMING OF PESTICIDE DISCOVERY AND DEVELOPMENT

-------
the more a company is dependent on new pesticide development for its
continuing income, the more emphasis this directed approach is given.
In 1970, the NACA study estimated that this directed approach represented
about 45% of all screened compounds. Because of the increased cost of
R&D and the necessity to have a greater percentage of successes to failures,
it is expected that this selective approach to synthesis will become more
important. This approach is not likely to result in the development of
fundamentally new classes of pesticides.
The primary screening for all types of compounds is a relatively
simple operation requiring skill in the interpretation of results. For
herbicidal activity for instance, the compounds are applied to a variety
of plants which are grown in flats in a greenhouse. These plants include
both weeds and crops. Herbicidal activity is present, simply, if the
compound selectively inhibits the growth of one or more of the plants.
Primary screening usually takes about six to eight weeks. About 7,000
compounds are screened for every successful commercialized product.
About 90Z of the compounds fall out in this first screening. Two or three
biologists supervise this primary screen which is mainly performed by
technicians. Although the process is tedious and time-consuming, both
technicians and supervisors must be skilled in recognizing subtle evidence
of biological activity which characterizes potential commercial successes.
According to the NACA survey, about 27% of all compounds screened are
screened for all types of pesticidal activities including herbicides,
insecticides, fungicides, and others. About 24% are screened only for
herbicides, 20% only for insecticides, and 15% only for fungicides. The
remainder are screened for other more specialized uses. The interest
expressed by many companies in emphasizing herbicide activity has increased
since the mid sixties.
Secondary and tertiary screening involves similar activity but with
more careful examination Involving a greater variety of plants and condi-
tions. This process takes between 8 and 12 weeks and in many companies
involves 6 to 8 biologists, entomologists or plant physiologists. It
eliminates another 90% of the compounds. Various chemical concentrations
are examined at this stage along with types of applications, e.g., direct
leaf applications, application to the soil, etc. At this stage the
scientists attempt to determine the mode of action involved in any pesticidal
activity present. If they believe that possible modifications to the
structure of the compound would be more effective in the mode of action,
a modified compound is synthesized and screened. About 700 compounds go
through this secondary and tertiary screening for every successful product.
At the end of the secondary and tertiary screening there is a review
of the products which have survived this stage. This is usually done by
a group of people representing various disciplines of pesticide development
including representatives from chemistry, biology, toxicology, environment,
marketing and process development. Although the compounds under considera-
tion have not been tested in many of these areas, knowledge and experience
with similar compounds will aid in the decision-making process. The
purpose of this review is to define lead compounds which deserve further
30

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investment for laboratory and field testing. At this time synthesis
chemists devote some of their efforts to the development of analogs
and homologs of the particular compounds. Also at this time patent
protection is initiated.
2. Secondary Biological Evaluation
Resynthesis of larger quantities of lead compounds begins after this
review period. The purpose of this resynthesis is twofold: to obtain
the necessary amounts of compounds for laboratory, toxicological and
field testing, and to obtain very preliminary process development data
to help determine the projected cost of producing the lead compounds.
This synthesis usually goes on for about 20 weeks and involves three
or four chemists. At the same time preliminary laboratory work is being
done to obtain initial toxicological data. This information will help
in the next review of these compounds and will also determine how the
compound should be handled in future laboratory and field testing for
the safety of the personnel involved. Accordingly these tests include
primarily acute oral and dermal toxicity tests. This preliminary
toxicity testing takes from 15 to 25 weeks.
At this time another review of the lead compounds is made to assess
the information provided in the toxicity and process development work.
An important factor at this point is the projected cost of producing the
product if they proceed with development to commercialization. The
marketing personnel are asked to assess the competitive costs necessary
to enter the market at the time of projected commercialization. This is
compared to the cost estimates provided by the synthesis and process
development personnel based on their preliminary work. If the projected
costs of producing the compound is greater than products already on the
market or projected to be on the market, the project is dropped. If the
projected costs are conducive to further development the toxicity of the
compound is assessed to determine whether the toxicity is significantly
higher than its projected competitors. High toxicity would make registra-
tion, marketing efforts, and consumer acceptance more difficult. About
one in 7 compounds pass this decision-snaking point.
For those compounds that have received a go-ahead decision, process
development work is extended to include initial formulation work. At
this point about 10-20 pounds of lead compounds are made. Some of this
amount is then used for initial small plot field tests. The purpose of
this initial field work is to confirm the bioactivity of the product,
i.e., its usefulness as a pesticide. Up to now the compound has only
been tested in a greenhouse. Although the size of these small plots
limits application to only several rows in parallel, this enables
observation of the compound under various soil and weather conditions.
At the end of the small plot field testing another review is made
by the R&D staff to determine which compounds deserve further Investment.
This decision is based mainly on the efficacy data acquired in the small
plot field tests although environmental factors are considered at this
31

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time. (If a compound seems to be environmentally unsound or If toxicity
is high, the go-ahead decision is reconsidered.) About one in 10
compounds are chosen for further development at this time—those for
which efficacy and costs make the compounds sufficiently attractive
to warrant the expense required for registration. At this time the
decisions are made as to which compounds need large scale field testing.
Those that do will require the large investment for an experimental use
permit.
Once this commitment is made to go ahead, with the compound as
a potential product, the small plot field tests on the lead compound are
extended to include the required efficacy and residue data necessary for
the experimental permit. Additionally at this time they start the two-
year toxicology tests that^are required for full registration. Six months
of data from these toxicology tests are necessary for experimental permit
application. After compiling the data from the first six months of the
toxicology tests, along with the data from efficacy and residue tests,
the experimental permit application is prepared and submitted.
3.	Experimental Use Permit
On the average, 7 months are required for approval of an experimental
permit. This may include resubmission of data required by the first
review of the experimental permit application by EPA. Many companies
start arranging for the field work while the experimental permit applica-
tion is being reviewed. Several of the companies, however, have had bad
experience as a result of obtaining commitments from participating
farmers and institutions, and producing enough compound for the forthcoming
field testing on a pilot plant stage, and then finding the approval on
their experimental permit has been delayed past the growing season. This
results in a loss of money, time, and the potential cooperation of
farmers in next year's field program. Most companies submit their
application for experimental permit as quickly after the last growing
season as possible, i.e., September, so that experimental permit can be
approved by January or February. This gives the company time to obtain
the necessary materials and cooperation for their large-scale field program.
4.	Field Testing and Data Gathering
The duration of the field testing program varies between 18 and 24
months. This includes a required two seasons for testing plus 6 months
for data compilation and analysis. The duration required for large-
scale field testing is increasing because of the number of regional
locations required and the fact that pesticide companies can no longer
count on universities for free testing. Industry uses land which they
rent or lease from private owners, or land which they have purchased
to be used on a continuing basis. Purchasing land is sometimes difficult
to justify since each new product demands different regional locations
of pests for testing.
32

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The following areas are among those Investigated In the large-
scale field testing program:
Efficacy—The requirements for full registration require data on
the efficacy of the product in solving the pest problem in the various
regions in which the product will be used. At times this could involve
50 locations.
Application rates—The large-scale field tests determine the
optimum rate of application as well as the optimum method, e.g., aerial
spraying, soil application, etc. This information will be used later
in formulation studies.
Crop residue—The determination of residue and metabolites in the
crop are done in the laboratory but the crops must be harvested at the
various locations of the large-scale field tests. Samples of the crops
are often frozen at the time of harvest and sent to nearby laboratories
for analysis.
Crop rotation—The uptake of the compound and its breakdown products
by successive crops in rotation is tested in the second season of the
field testing program.
Pathways and levels of ecological penetration—Information on runoff,
dispersion of the compound from aerial spraying, entrance into surficial
and groundwater systems are assessed for both the compound and its
breakdown products. This Information is related to environmental labora-
tory work which is going on in parallel with the field program.
The laboratory environmental effort includes analysis of data and
samples from the field program. Additionally such studies as bioconcentra-
tion Investigations in aqueous systems are done at this time, using
indicator organisms such as trout or quail, depending on the particular
pathway of ecological penetration which is indicated in the field program.
This environmental laboratory work usually begins Immediately after the
first season of field testing and continues on approximately 8 or 9 months
after the end of the field testing program. The total duration for these
laboratory environmental studies is about 18 months.
The two-year toxicity tests which were begun prior to the application
for experimental permit are generally completed about half way through
the field testing program. These toxicity tests include oral LD50 and
subacute toxicity feeding tests as a minimum, but generally also require
reproduction studies, teratogenicity studies, metabolism studies,
mutagenicity studies, and other toxicological tests. These tests often
require from one to two years. Human hazard evaluation includes eye
irritation, dermal irritation and tests for inhalation. The
entire duration of these toxicity tests is about 2 1/2 years, including
6 months required for analysis of the data.
33

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5. Registration
The information compiled from the toxicity tests, field program,
and the laboratory environmental work is compiled in an application for
full registration. Upon receipt of the application EPA reviews the
information and compiles all questions from individual reviewers. These
are then sent back to the applicant as additional data which are required.
Sometimes this requires additional testing, other times it requires
merely additional supportive data which was not included in the original
application. Upon receipt of the additional information, EPA then reviews
the entire application and makes its determination. The average duration
of this review process is 15 months.
6. Process Development and Marketing
While the toxicity and environmental testing are being performed,
continuous low level efforts are also being expended on marketing and
process development including formulation. Once full registration is
obtained these efforts increase. It is usually two years from the date
of registration to commercialization, if the plant construction has
begun before registration. Because this represents such a large expendi-
ture (as much as 20-30 million dollars), many companies wait until they
receive reasonable assurance on registration before they start plant
construction. If they wait until after full registration to begin plant
construction it is usually four years before the product can successfully
penetrate the market.
C. TRENDS IN R&D ACTIVITIES
1. Costs
The average estimated cost per compound for discovery and development
is $7.6 million including the costs of compounds which were not commercial-
ized. The average cost of the development of the individual compound is
$1.8 million. These costs are estimated by industry considering current
registration requirements and other research and development costs and
represent a hypothetical compound presently being developed. The NACA
study reported in 1970 that the cost of discovery and development of
a pesticide was approximately 5.5 million dollars and indicated a wide
range of costs were reported among the companies participating. The
companies participating in our study also Indicated a wide range of
costs, as shown in Table 1. The cost for similar inventions and
developments is perhaps best represented by the cost to develop a new
pharmaceutical product, i.e., a specific new drug. In the past few years
this cost is estimated to be approximately $6-8 million.
The reasons for the increases in cost vary considerably with
Individual companies but generally include the increase costs of registra-
tion requirements. Registration requirements account for about 20% to
30% of the entire pesticide budget in most companies. The rest is spent
on plant pollution controls, marketing and process development. Plant
34
Arthur D Little Inc

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TABLE 1
ESTIMATED COST OF DISCOVERY AND DEVELOPMENT OF A PESTICIDE
Total R&D Cost Per Successful Compound (Including
Rejected Compounds)
RANGE	ESTIMATED AVERAGE
$12,000,000 - $4,000,000 - 1974	$7,400,000 - 1974**
5,500,000 - 1970*
6,000,000 - 1969*
3,400,000 - 1967*
*
NACA survey.
**
From 22 companies participating in this survey.
35

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construction accounts for the largest part of the budget, about $20-30 million
per product as mentioned earlier.
The overall costs of the entire pesticide development have increased.
Some of the factors include:
(1)	the growing sophistication of the pesticide industry,
(2)	the increased competition among products, and
(3)	the increased costs of materials and labor.
The various stages of pesticide and development process have not all
increased in cost to the same degree. The areas of R&D which are felt
to account for the largest increases are:
(1)	Field Testing
Field testing accounts for about 30% of the total cost required to
bring an individual compound from synthesis to registration. Recent
increases are due in part to the increases in number of regional crop
areas needed to fulfill registration test requirements. Some companies
report 50 to 100 or more different field tests are required in different
parts of the country for major crops. Combining this with the number of
tests required at each site (about 5) can lead up to 500 tests being
done at the same time for each compound undergoing field testing.
(2)	Maintenance of Existing Products
The NACA study in 1970 reported 25% of the R&D budget was being spent
on the defense of existing products (for reregistration and for additional
uses of the product) compared to 13.4% in 1967. Most companies today
report 30%. The increase from 1967 to 1970 was probably due to the re-
registration of all compounds according to the finite residue requirements.
A wide range of figures was obtained for the percentage of R&D budget
spent on reregistration. This percentage may depend in part on how
"hungry" a company is for new products, i.e., how long ago the company
came out with its last product. If no new products have been developed
lately, more effort is spent on the search for new products. If the
company has recently been successful in developing a product, more effort
will be spent on developing new uses for it.
(3)	Personnel and Equipment Costs
Innovative activity has changed over the years because of increased
knowledge of structure versus biological activity and the mechanism of
action of pesticides. This has led to a need for more educated manpower
and more sophisticated equipment. Electronic equipment such as high
resolution mass spectrometers and sophisticated data retrieval systems
have become important to innovative activity. Additionally, the educa-
tional and skill requirements of the scientists involved in R&D are
36

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Increasing as the knowledge of the mechanism of the biological activity
of pesticides becomes more of a factor in discovering a successful
compound (specific manpower trends will be discussed in the following
section). These increases in expenditures for equipment and manpower
are resulting in a higher cost per man year for the R&D process. The
data from the NACA survey yields a figure of $65,000 per man year in
1970 as opposed to $47,400 per man year in 1967. The current estimated cost per
man year obtained from industry in our study is somewhat lower, about $55,000.
Some information was gathered in this study on the costs to develop
existing products. Table 2 shows average costs to develop compounds which
were registered in the late 50's as compared to compounds registered in
the late 60's. The costs cannot be directly compared to estimated costs
discussed above because these costs of existing compounds reflect the
requirements of the years preceding the date of registration rather than
anticipated costs at that date.
The figures show that one million or less was spent per successful
compound in the late 50's and that the costs average as low as $.2 million
in 1956 up to and including the first registration. In the late 60's about
$1.5 million was spent per successful compound, until 1969 when the cost
jumped to $3.2 million, reflecting to some extent the finite residue
requirements.
Some of the expenditures per year for various areas of pesticide
research provided by one specific company are shown in Table 3. Although
the amount of yearly expenditures on insecticides and herbicides vary
considerably among industry, some of the other areas of expenditures
shown in this table may be more representative. These include the amount
spent on basic research done per year in the herbicide and insecticide
area, $20,000 aitd $30,000 respectively. This amount may reflect a general
industry policy to study biological mechanisms only as they relate to
specific lead compounds, or potential chemical analogs of these compounds.
Very little is done in most companies on basic research which would lead
to isolated naturally occurring compounds or other innovative methods of
control. Most companies questioned preferred that this badic research
be done in government or universities.
The amount of R&D as a percentage of sales is often given as an
indication of industries' commitment to research. Table 4 shows the
annual research expenditure per company in dollars and as a percent of
total sales. Pesticide R&D was found to double in dollars from 1965 to
1974 while remaining about the same as a percent of sales. The general
impression gained from industry is that this percentage will continue to
hold steady for industry in general, although it will vary considerably
between companies depending on how "hungry" a company is for new products
or committed to the field. By comparison, the pharmaceutical industry
devotes about 10% of its sales to R&D efforts, the heavy chemical industry
devotes about 2-4%.
37

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TABLE 2
COST OF DEVELOPING COMPOUNDS WHICH HAVE BEEN REGISTERED*
1956 1958 1959 1965 1966 1967 1969
0.3 m 1.0 m 1.5 m 1.5 m 1.6 m 3.2 m
from 22 companies In this survey.
TABLE 3
ESTIMATES FOR PORTIONS OF R&D BUDGET BASED
ON ACTUAL COMPANY DATA FOR 1974
Per Year
Herbicide Basic Biochemical Studies
$
20,000
Insecticide Basic Biochemical Studies

30,000
Fungicide Product Research

10,000
Herbicide Product Research

200,000
Insecticide Product Research

70,000
Environmental Studies for Above Product
Research
460,000
Formulations

290,000
Pollution Control for Production Plant

530,000
$ 0.2 m
*
Data
38

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TABLE 4
ANNUAL PESTICIDE RESEARCH EXPENDITURES PER COMPANY
Average	High	Low
1965 $1,363,000	$1,902,000	$250,000
1974 $3,212,000	$6,000,000	$1,000,000
As Percentage of Sales
Average High	Low
1965 5.4% 10%	4%
1974 5.9% 8%	3.25%
Source: this study
39

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2. Timing
The timing of the R&D process has changed in three general ways:
(1) the duration of the R&D process has lengthened, (2) individual areas
of effort within the R&D process have increased in time and (3) there has
been a re-ordering of the timing of various effects within the process.
Figure 3 shows the duration of the R&D development process for representa-
tive actual products developed by industry in the 1950's and 1960's.
Some of these indicate the duration of effort between synthesis and
registration, while others indicate the duration of effort between
screening and marketing. The averages (considering only those durations
from synthesis to registration) for the yearly Intervals between the
1950's and the present show an increase in the duration of the R&D process.
Between the years 1950 and 1960 the average length of time needed for
development of a pesticide (including registration) was 2.75 years.
Between the years 1955 and 1965 this increased only slightly to an
average of 3.0 years. A more significant increase is found between the
years of 1960 and 1970 when the average duration for the development
process was 4.6 years, increasing to 7.0 years between the years 1965
to 1975. The cause of the overall increase in timing can be seen in the
increased time needed for specific efforts within the R&D process. In
the late 1950's It took approximately 1-4 months to do both the metabolism
and the toxicology tests. Now these are part of a 2 1/2 year testing
program. The timing required for field testing has increased since it is
done now in two stages, one in preparation for the experimental permit
and the other in preparation for full registration. The combined efforts
for field testing often consumes about 2-3 years of development time.
After all the field testing and other testing is done, the time required
for registration is also significant. Table 5 shows the average time
spent between submission of the application for full registration and the
final decision by EPA. This time includes the submission of any addi-
tional information required. The time required for registration has in-
creased by a factor of 4 from the late 1950's to the early 1970's. This
has been a steady increase with the largest rise occurring from the
early 60's to the late 60's.
The shift in timing of individual efforts within the R&D process has
generally occurred as a trend towards earlier compilation of data on a
wider variety of subjects. This enables early decision-making to be
supported by the largest amount of data possible. Like field testing,
some of the efforts are divided into two stages: one to give an early
indication to include in decision-making, and two to support the applica-
tion for registration of a candidate compound. Toxicology, for instance,
involves three stages of testing: early decision-making, application for
experimental permit and application for full registration. This division
of effort decreases the efficiency of the R&D effort and adds to the
overall time involved.
Figure 4 represents the duration of development of "hypothetical"
compounds or estimated R&D timing for "hypothetical" compounds provided
to us during discussions with industry. (This differs from Figure 3

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Compound 50	52
A	syn	
B	syn	
54
FIGURE 3.
56
DURATION OF THE R&D DEVELOPMENT PROCESS FOR REPRESENTATIVE
PRODUCTS DEVELOPED IN TEE 1950's AND 1960's
58
year
60	62 64
66
68
Teg
Teg
70
72
74
C
D
E
F
G
H
I
J
K
L
M
N
0
P
syn-
Teg
syn-
Teg
screen-
Teg
syn-
syn-
syn
Teg
Teg
screen-
Teg
-market
synr
syn-
synr
Teg
synr
screen-
screen-
Teg
Teg
Teg
-market
-market
Average Duration
From Synthesis to
Registration	
1950-60
1955-65
1960-70
1965-75
2.75
3.0
4.6
7.0
syn-
-reg
Q
screen-
market

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FIGURE 3 (Continued)
.>
N>
year
Compound 50 52 54 56 58 60	62 64 66 68	70 72	74
R	syn ¦ ¦ reg
S	syn	~	reg
T	syn	reg	
U	syn	reg
V	syn	reg
W	syn	reg
X	Syn(excluding international re®
testing)
2nd
Y	screen	market
Z	syn	reg
AA	syn	reg
BB	syn	reg
CC	syn	reg
DD	syn	reg
EE	syn	^

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FIGURE 4. ESTIMATES OF DURATION OF DEVELOPMENT FOR
HYPOTHETICAL COMPOUNDS
Compound	52 5 4 56 58 60 62 64	6 6	6 8	7 0	72	74
	"¦		year
A	syn	reg
B	syn	market
C	syn	market
D	screen 	market
E	syn	reg
F	NACA	, ^
screen 	market
G
H
I
syn	reg
syn	reg
5 J	syn	market
K	syn	reg
L	syn	market
M	syn	market
N	Average Duration from	syn	reg
0	Synthesis to Registration	syn	rfig
P	1960-70 4.3	syn	reg
1965-75 8.1

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TABLE 5
AVERAGE DURATION OF REGISTRATION REVIEW INCLUDING
SUBMISSION OF ANY ADDITIONAL INFORMATION REQUIRED
(Months)
1955-1960	3.5
1960-1965	5
1965-1970	10.8
1970-1975	14.8
TABLE 6
NUMBER OF R&D PERSONNEL IN TYPICAL COMPANIES
High	Low	Average
I960 100	6	38.8
1965 95	10	54.0
1970 75	18	50.5
1974 188	32	78.5
Source: This study
44

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which represents actual historic data.) Industry estimated that the time
required for discovery and development between 1965 and 1975 was 8.1 years,
or about one year more than the time needed for those products registered
in the early 70*s. This additional time reflects current and anticipated
development requirements for a hypothetical compound in the process of
development today.
3. Manpower
Table 6 shows the average number of professional persons working in
representative pesticide companies in 1974, including professionals and
technicians and non-technical persons. This average, 78 persons, indicates
that the number of professional personnel in the pesticide R&D area has
increased significantly since 1970. Generally professionals comprise
about 50-60% of the R&D staff with the rest non-technical hourly labor
and laboratory technicians. Much of the hourly labor as well as a
significant portion of the professional labor is occupied by field testing
which, in total, accounts for about 20-25% of the manpower.
The most prevalent trends in manpower seems to be the reshuffling
of personnel according to the changing priorities in each company. Some
companies have transferred individual scientists, e.g., transferring
synthesis chemists to defense of existing products, while others have
changed the direction of whole groups, e.g., changing the focus of the
biochemical area to help answer the questions posed by the PR 70-15
regulations. The environmental regulatory work on new products and the
overall defense of existing products have absorbed most of the shifts
in staffing, with the areas suffering the most being new product develop-
ment, i.e., synthesis and screening. In testing areas that demand
personnel beyond the existing capacity of a company, the work is done on
a contract basis rather than by hiring additional personnel. Toxicology
is one example of a testing area which is often done by contract.
No significant changes in the types or numbers of staff were
reported by industry in our study, although a significant increase in
more highly educated scientists, especially scientists with Ph.D.'s,
was reported for 1970 in the NACA study. Several companies mentioned
that they were trying to keep costs down by hiring less experienced
persons just graduating from school, or by not hiring highly specialized
Ph.D. scientists.
The cost of R&D scientific manpower in the pesticide Industry is
estimated to be about $50,000 per man year. This is comparable to
scientific manpower costs in many other industries, but slightly higher
than that estimated for the pharmaceutical industry of $40,000 per
man year.
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D. DECISION MAKING IN PESTICIDE R&D
Because of increases in time and cost, the decision as to which
compounds to develop becomes more important as companies seek to increase
their ratios of successes to failures. The decision making comes earlier
in product development, and more frequently. This decision making is
supported by more efficacy, cost, and safety data, since the increase
of risk has led management to require more confirming data both in
technical areas and in market areas in order to decide to go ahead with
a particular compound.
The relative weights assigned to the decision making factors shape
the characteristics of the pesticides that result from the development
process by selective screening according to those characteristics. The
companies contacted in this study rated the following factors in order
of importance in their decision making:
1.	Efficacy
The performance of a compound in solving a particular pest problem
better than other compounds currently in the market is given highest
priority in decisions concerning research and development of compounds.
Most compounds are dropped on the basis of (1) selectivity, toxicity,
and phytotoxicity, (2) inability to eliminate a greater fraction of the
pest problem in equal or less time than current products on the market,
(3) instability of the compound in shipment or in the field leading to
lack of reliability of effectiveness, (4) ineffectiveness of the compound
in the required range of soil and weather conditions.
2.	Cost
If a company foresees that the proposed cost of producing a compound
is significantly higher than competitive products on the market, this
compound will be dropped. The process development work which helps
determine the cost of the compound is being done earlier in the develop-
ment process to assist in this decision. This also puts an added burden
on marketing personnel who must assess price fluctuations further in
advance.
3.	Volume of Market
As discussed previously in regard to major and minor markets, the
volume of market needed to develop a potential product varies with the
amount spent on the R&D process by individual companies. Some require
a $10 million market while others require $500,000 as their minimum
market for deciding to go ahead with a potential product. Profitability,
of course, is included in the assessment of the volume needed for the
return on a product investment. The profitability however does not vary
to the same degree as volume, i.e., it cannot compensate for lack of
volume in obtaining the needed return on the product investment.
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Product development costs for minor uses are usually the same as
for major uses since the same development and registration requirements
apply to both. In deciding which compounds to develop, some companies
eliminate any compound which can only be used on a minor market. Many
companies state that the IR-4 programs to develop minor use products
needed in individual states has not been adequate in compensating for
much of the product development costs. Thus reluctance to develop
pesticides for minor crops because of high development costs are a growing
concern to some growers' associations and states. One state asked a
company we contacted to stockpile a specific compound needed to control
a mosquito that had a potential in spreading disease. Because the costs
of product development and the sporadic nature of the need for the product
and thus the unreliable return on the investment, the company decided that
It was too expensive to develop and stockpile the product and it could not
meet the state's request. Some companies indicated that they develop a
minor use product only if one of the following conditions are met: (1) If
it had already been registered for a major use; (2) if it can be used
for public relation purposes, i.e., for keeping good will among the
consumers who will use other products produced by the company; and (3)
if the minor use product is particularly easy to produce.
4. Environmental and Safety Factors
Some companies say that environmental factors have moved back in
the decision-making process to become factors in the earlier decision
point. The environmental considerations Include requirements that the
product have a reasonably rapid breakdown in soil and that it not enter
the food chain. Others say that if the product is highly toxic they will
hesitate to proceed with the development of the compound. Most of these
considerations are based on an increase in environmental awareness on
the part of both industry and the consumer. Most companies do not feel
that safer compounds have an easier time in registration because the
same data and testing is required for all compounds. There is a fear,
however, that given two equally effective compounds, preference in
Registration may ultimately occur because of safety or environmental
concerns. Any perceived difficulty in registration is carefully consider-
ed but in itself will not prevent the development of the compound. Some
companies seem to fear the possibility of legal suits based on environ-
mental and safety factors brought by consumers more than any additional
registration requirements or possible restrictive use under the law.
Several companies in fact said that self-regulation on the basis of
this anticipation of consumer legal action would work equally as well
as the present law.
In summary, the decision on which compounds to develop Is becoming
more Important as companies try and Improve their success to failure
tatlo. Efficacy and cost are the most Important. More compounds get
put "on the shelf" for failing in these areas than any others. Anticipated
Volume of sales is next in Importance with decisions favoring major use
markets. Toxicological hazards will slow down product "go ahead decisions"
primarily because of consumer acceptance of any anticipated extra
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registration requirements are considered but in themselves do not prevent
the development of a compound.
E. TRENDS IN PRODUCT DEVELOPMENT AND INNOVATION
Table 7 shows the average number of new compounds developed and
the average number of registrations obtained for representative companies
contacted in this study. Between the years of 1960 and 1965 an average
of 5.6 compounds were developed per company. Between the years 1965 to
1970 an average of 2.6 compounds were developed per company. The sharp
decline in this average may be due in part to a decrease in activity
during the years following the issuance of the finite residue require-
ment during which time industry spent much of its time testing and re-
registering its existing products. This decline, however, may also be
due to four other factors: 1) fewer compounds are in the process of
development due to caution on the part of decision makers in regard to
higher costs for the product development process; 2) minor use markets
are not receiving attention; 3) a general decrease in the productivity
of the R&D process is occurring as a result of the necessity to place
effort in the defense of new and existing products, 4) simple, easily
developed compounds have already been discovered.
The trend indicated in the number of registrations obtained per
company (also shown in Table 7) indicated that companies are continuing
to obtain registrations for new uses and new formulation for existing
products at the same rate. Between the years 1960 to 1965 an average
of 90 registrations were obtained compared to 71 in late 1960's and
75 between the years 1970 and 1974. These registrations include addi-
tional uses for existing products, new products, new compound registra-
tions, formulation registrations, and others.
1. Decreases in Particular Types of Compounds
Several companies mentioned that they had gotten out of the insecti-
cide R&D area because of several reasons which will be simplified here
for the sake of brevity. Companies have had less success in developing
insecticides because new functional groups possessing insecticidal
activity have been generally exhausted in the search for new compounds.
Additionally, the market for insecticides has been around a longer time
and is saturated with inexpensive, non-proprietary compounds which make the
cost of producing insecticides a very important factor and one which tends
to eliminate compounds early in the development process. Herbicides
seem to represent a larger market where higher profits can be expected as
extensively. Those companies that have been successful in developing
insecticides, however, are staying in that area. Only companies that
were only marginally successful in insecticide areas have been affected
by this trend. Fungicides have also been eliminated from the screening
done by many companies. This is mainly because most fungicides represent
minor markets. Additionally, they are generally more specific than either
insecticides or herbicides and thus cannot be extended to the same number
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TABLE 7
NUMBER OF NEW COMPOUNDS REGISTERED PER COMPANY
1960 - 1965	1965 - 1970	1970 - 1974
(estimated—not
enough data available)
5.6	2.6	2.0
Range 1 to 19	Range 0 to 6	Range 1 to 4
TOTAL OF REGISTRATIONS PER COMPANY INCLUDING
NEW USES. FORMULATIONS, ETC.
1960 - 1965	1965 - 1970	1970 - 1974
90	71	75
Source: This study
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of additional uses. Industry Is also avoiding areas that can easily be
anticipated to represent large registration requirements that are not
compensated by large volume markets. For Instance, the rapid distribution
of aquatic herbioides into the ecosystem and the extensive environmental
testing needed for registration, are making some companies avoid this low
volume market.
2.	On-the-Shelf Compounds
There is a general feeling among those outside of the industry that
there may be compounds on the shelf which companies are holding back
until registration requirements become stabilized or less expensive. This
was not found to be true. Any compounds on the shelf are there because
they were eliminated in the decision-making process as either too costly,
non-effective, or unsafe. Furthermore, all decisions on developing a
compound are based on a precise timing for entrance into the market.
Compounds cannot be held back if a company expects to gain its projected
return on development since a competition may beat them to the market with
a better product.
3.	Biological Controls
In regard to decision-making factors discussed above—efficacy, cost,
market volume and safety—industry in general does not consider biological
controls worth pursuing.
Only one company, Zoecon Corporation, was found to be devoting their
major effort to the development of hormonal control methods. Other
companies in the pesticide industry are watching this firm closely to see
if such biological controls can be a successful venture if pursued
vigorously. The degree of involvement of other companies in the biological
control field varies with the type of compound considered, i.e., whether
it is a synthesized analog of a natural occurring substance, e.g.,
juvenile hormones or irtiether it is the naturally occurring substance
itself, e.g., bacteria and viruses. In general industry regards biological
controls as being the latter. About 20% of the companies contacted in
this study are maintaining some level of effott in the "synthesized
biological" controls. Most of the work is being done in juvenile hormones
and plant growth regulators. Work being done is on a low level of
effort, usually as a sideline of on-going R&D. Some companies are main-
taining effort in juvenile hormones so that they will have gained
sufficient experience when they feel the market is ready. Others look
into these types of controls as part of their basic research, looking at
different modes of actions in major pests. Some companies have been
working in the juvenile hormone area, have decided it is not a profitable
venture and are eliminating that area of research.
The most prevalent attitude towards naturally occurring biological
control methods is the attitude of "vigilance." This is expressed in
several ways, i.e., companies are "keeping track of what is going on" or
"keeping up with the literature" or "leaving the door open for research
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in that area" but waiting to see how well others do in the business.
The lack of effort in the more innovative naturally occurring
biological controls is due to several problems foreseen by industry in
that area:
(1)	The biggest problem seems to be lack of patent protection
for bacteria and viruses. After a company has made large expenditures to
register a bacteria or viruses it is faced with the possibility that
other companies can then register the same bacteria or virus and undercut
the price since they do not have to make up for registration costs. This
is compounded by the fact that the active biological ingredients may be
easy to make and thus the market is easily entered. BT, for instance,
can easily be made by standard fermentation processes. This is further
compounded by the fact that the entire market for BT presently is estijnated
at only two to three million dollars. (The market for viruses is still
uncertain.) A dissenting opinion on the problem of patent protection is
that the formulation of naturally occurring biological controls is a
challenge in overcoming problems of stability, potency and reliability.
A successful formulation which solves these problems can be patented and
can be used to maintain a continuing place in the market. Others hope
the 3(c)(1)(D) clause requiring the payment for use of registration in-
formation will supply some protection, and prevent some "me too" companies
from entering the field.
According to some industry spokesmen, some biological controls
developed by the government are currently sitting on the shelf because
the lack of exclusive patent protection. If a biological control is
discovered in the U.S.D.A. labs in Beltsville, Maryland, they are passed
on to other U.S.D.A. labs for feasibility tests and then are available
to industry to develop commercially. However, the lack of patent protec-
tion or non-exclusive rights to government developments causes many
industries to hesitate in taking advantage of this opportunity. Some
companies recommend that competitive bidding be used to provide exclusive
rights to industry for biological control approaches discovered by govern-
ment laboratories.
(2)	The second major cause for lack of effort in the biological
control field are problems in formulation stability and reliability that
are causing the costs of development of naturally occurring biological
controls to go up. Viruses, in particular, involve problems in stability
and packaging. Companies involved with the development of viruses say
that these problems of stability are a much greater Influence on timing
and costs of development than any registration requirements.
(3)	Consumer acceptance is the third major problem in the biological
control field. The consumer may not be willing to compensate for the
added costs of development of these biological controls, or the added
cost of any specialized application techniques. Even without these
added costs, industry expects that a great deal of education will be re-
quired before the farmer will accept naturally occurring biological
controls. For instance, controlling the sweet corn earworm with BT will
assure that the earwotm does not eat the corn but the consumer will find
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enlarged diseased earworm still on the corn when it reaches the market.
This is a general problem with BT since it does not eliminate the
presence of the Insect for several days, although it does almost immediately
stop it from consuming the crop.
(A) Most companies feel that biological controls can only be used
on a regional basis as part of the integrated pest control program. They
expect that increased government management and control of pest programs
will be necessary before biological controls can be used successfully.
Some companies feel that only government programs such as that of the
U.S. Forest Service represent viable markets for these controls, and they
do not expect, or desire this amount of government control of private
agriculture.
(5) Lastly, those companies which are not actively involved in
biological control feel that EPA will and should be cautious about
possible hazards to human health presented by naturally occurring biological
* controls, both BT and the viruses that are currently being investigated.
The fact that the pesticidal mechanisms are not fully understood in these
compounds is a cause for concern. Even the development of genetically
resistant crops may involve chemicals which are present in the crop.
These chemicals are unknown and untested and are transported directly to
the consumer. Also, introducing viruses into the environment even in
small plot field testB is felt to be less safe than chemical compounds
since the viruses can propagate and thus cannot be removed from the
environment via the usual method of destroying the crop. The general
mistrust for naturally occurring biological controls on the part of many
companies can be summarized by one R&D manager we contacted who stated,
"I'd rather take a bath in DDT than stick my finger in BT."
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IV. LEGISLATIVE ACTIONS AND THEIR IMPACT
A. INTRODUCTION
The United States Is and has been committed by law, regulation, policy
and tradition to insure that the food supply of the nation is safe, clean
and wholesome and to protect the safety and health of the direct and in-
direct users of pesticides and the consumers of products which depend upon
pesticide use. The quality of the total environment—soil, water and air—
in which food is grown, processed and consumed controls to some degree
the quality of our food and our health. Contamination of these natural
resources by pesticides, their residues, and related materials not only
affects the quality and safety of our food, but also affects environmental
values such as wildlife preservation, recreation and aesthetics. Thus,
the regulation and control of pesticide has broad influences over the
public health, safety and welfare.
Federal regulation of pesticides began with the Insecticide Act of
1910; this Act was intended to prevent fraudulent efficacy claims and to
authorize the seizure and banning of compounds dangerous to health.
The great increases in variety and use of synthetic chemical pesti-
cides during and after World War II resulted In the passage of the Federal
Insecticide, Fungicide and Rodenticide Act (FIFRA) in 1947, a law designed
to regulate the marketing of "economic poisons" and "devices." These terms
were originally defined as "economic poison—any substance or mixture of
substances intended for preventing, destroying, repelling or mitigating
any insects, rodents, nematodes, fungi, weeds and other forms of plants
or animal life, which the Secretary (of Agriculture) shall declare to be
a pest and any substance or mixture of substances intended for use as a
plant regulator, defoliant or desiccant." "Devices" were defined as "any
instruments or contrivance intended for trapping, destroying, repelling
or mitigating Insects or rodents, or destroying, repelling or mitigating
fungi, nematodes, or other pests, but not including equipment used for
the application of economic poisons when sold separately therefrom."
FIFRA was amended by the Nematocide, Plant Regulator, Defoliant and
Desiccant Act of 1959, and amended again in 1961 and in 1964.
Under FIFRA (administered by the Department of Agriculture) pesticide
chemicals could not be distributed or sold in interstate commerce unless
they had been shown to be safe when used as directed and effective for the
purpose claimed on the label.
Any residues remaining on food or feed could not exceed the safe
tolerance level established by the Food and Drug Administration in Imple-
menting the Pesticide Chemicals Amendment and Food Additives Amendment
of the Food, Drug and Cosmetic Act. The purpose of this Act was to Insure
the safety of the nation's food supply by requiring that the residues
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remaining on food were shown (by the Industry wishing registration of
the pesticide) to be safe for the consumer before the pesticide could be
cleared for general use.
As pesticides came into ever-wider use, and their environmental as
well as their health effects became known, the federal government began
assessing and implementing the need for greater regulation of pesticides.
A broad range of environmental concerns were addressed in 1970 through
guidelines for studies to determine the impact of pesticides on the environ-
ment (PR Notice 70-15)—environmental data required as part of the applica-
tion for registration. In December 1970 the authority to administer FIFRA
was transferred to the Environmental Protection Agency as well as the
authority to establish tolerance levels for pesticides and residues for
food and food products. In October 1972, HR 10729, the Federal Environ-
mental Pesticide Control Act (FEPCA) or "FIFRA amended" was signed into
law. The implementation of FEPCA and its regulations is now proceeding
in accordance with the requirements of the law.
In this section of the report, we will briefly discuss the major
features of FIFRA and FEPCA, concentrating on those parts of the law and
subsequent regulations which have the greatest potential effect on re-
search and development activities in the pesticide industry. We will
summarily compare FIFRA and FEPCA, to the extent definitive regulations
have been promulgated.* Then we will address the specific and general
impacts of these laws and regulations on research and development in the
pesticide industry.
B. REVIEW AND COMPARISON OF FIFRA AND FEPCA
1. FIFRA
FIFRA provided for labeling which specified uses of pesticides with
appropriate cautions and warnings and prohibited the interstate sale
and/or shipment of economic poisons which were not registered, or were
misbranded or adulterated. Further, it was unlawful for anyone to detach,
alter or destroy pesticide labeling, to refuse to provide access to books
and records authorized in the Act to persons designated by the Secretary,
to provide false guarantees, or to use for his own advantage or to reveal
(in general) information relative to formulas of products obtained through
the registration process. FIFRA provided for the registration of economic
poisons, and the suspension or cancelling of the registration of an
economic poison wherever it appeared that the article or its labeling did
not comply with the provisions of the Act. FIFRA also outlined the review
and appeal process for registration. The law also called for maintenance
Several notices of proposed regulations under FEPCA were published in
the Federal Register during*this Investigation. We were not able to
obtain information on industries' views of the impact on R&D of these
r ecent chang es.
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of books and records on pesticide shipment and delivery by manufacturers,
distributors and others involved in selling pesticides. Enforcement
provisions were authorized as were penalties and seizure of illegal pesti-
cides. Imports were regulated to provide for inspection to determine
whether the products were adulterated, misbranded, or were dangerous to
health. Reregistration of pesticides was to occur at five-year intervals.
Regulations under F1FRA subsequently defined the labeling process
and label content, the procedure and requirements for registration, guaran-
tees, coloration and discoloration, adulteration and misbranding and en-
forcement.
The principal parts of FIFRA which affected research and development
activities in the pesticide industry were the regulations and requirements
Involving registration and labeling, the experimental use of pesticides,
and the establishment of tolerances.
a. Data Required for Registration
For the Department of Agriculture the applicant for registration
had to furnish documented proof to support the claims made for the proposed
product. Data required to support registration usually included the
following:
Toxicity Tests and Data
Toxicity tests on the proposed formulation were to be conducted to
show that the directed use of the product would not be injurious to ex-
posed man or beneficial animals when warnings and cautions are carefully
followed. The extent of toxicological data required varied with the
nature and proposed use of the product. Toxicity studies normally included:
Safety Data
•	Acute mammalian studies (oral, dermal, Inhalation, and eye
and skin irritation).
•	Subacute studies—oral - 90 days; dermal - 21 days;
inhalation - 14 days.
•	Other studies required in some cases included:
Neurotoxicity
Teratogenicity
Effects on reproduction
Synergism
Potentiation
Metabolism
Avian and fish toxicity
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Physical - Chemical Data
•	Boiling point
•	Flash point
•	Physical state
•	Density
•	Vapor pressure
•	Solubility
•	Stability
Efficacy Teats and Data
Biological tests under field and laboratory conditions were to be
conducted to show that the product would control the pests named on the
label, when used as directed, without causing significant adverse effects
to the crop or property being treated. The following factors were con-
sidered in determining efficacy:
•	Effectiveness
•	Phytotoxicity
•	Translocation by the plant or animal being treated
0	Persistence in soil, water or plants
•	Compatibility with other chemicals
•	A thorough search and evaluation of the data submitted as
well as other applicable data
Labeling
General labeling requirements consisted of:
•	Name of product
•	Name and address of manufacturer, registrant, or person
for whom manufactured
•	Net contents
•	Ingredient statement—name and percent (by weight) of each
active Ingredient, and total percent of Ingredients
•	Warning or caution statement—the label of any economic
poison had to show warnings pertaining to:
ingestion
skin absorption
Inhalation
flammablllty or explosion
•	The registration number assigned to the product
•	Directions for use which are adequate to protect the public
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Other required information in the registration process included:
•	Data to support any or all claims on the labeling
•	A complete statement of the composition of the product,
including the percentage by weight of each of the active
and inert ingredients, if such information does not appear
on the label
•	Any pertinent information about inert ingredients
•	Any other information pertaining to physical or biological
properties of the product, etc.
Petitions for registration filed with the Department of Agriculture
were reviewed and commented on by other departments of the federal govern-
ment. The Department of Interior reviewed all petitions for registration
of pesticides whose use patterns may have had an impact on fish or wildlife.
The Public Health Service of the Department of Health, Education and Welfare,
reviewed all petitions from the standpoint of human safety. The comments
of these two agencies were then forwarded to the Department of Agriculture
and were considered before registration was granted or refused.
Analytical method(s) suitable for enforcement purposes were to be
provided with the petition if suggested use patterns would result in
residues of the chemical on food or feed. The analytical method(s) and
the residue levels presented in the petition were evaluated and an opinion
on whether the proposed tolerance reasonably reflected the residue was
forwarded to the Food and Drug Administration.
b. Establishment of Tolerances
If the product was proposed for use in a manner which was likely to
result in residues In or on food or feed, the product was not registered
by the Department of Agriculture until a tolerance or exemption had been
granted by the Food and Drug Administration.
Tolerances under Section 408 of the Food, Drug and Cosmetic Act were
established on raw agricultural commodities. The criteria and data require-
ments for establishing tolerances are summarized below. The basic require-
ment was that the data and other information furnished, when evaluated as
a whole, established the safety of the proposed pesticide tolerance.
Chemical Data
The residue data must delineate the identity and magnitude of the
residues and must show that, under the proposed conditions of use, the
proposed tolerance is suitable.
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The analytical methods used to obtain the residue data must be valid
and must afford a measure of the total toxic residue.
Toxicological Data
The requirements for the two major types of tolerances—for
negligible residues and for residues (higher levels) are outlined below:
(a)	A negligible residue tolerance was onfe that was sufficiently
limited by the magnitude of the residue, extent of use, and
mode of use so that the levels of ingestion which result
were considered to be of little or no toxicological significance.
The safety factor (the ratio of residue level to level at which
toxicological effects occur) was usually about 2000 based on
9-day toxicity studies.
(b)	A tolerance for residues in excess of negligible residues
required the following data:
Acute Toxicity
•	LDjq in at least two species of animals
•	A description of the signs of toxicity
Short-Term Toxicity (subacute toxicity)
•	At least two species, one a non-rodent
•	Duration, 90 days
•	At least three damage levels plus a control group; one
dosage level should be toxic
•	When 9-day studies are designed to continue for long-term
toxicity studies, sufficient animals must be started to
supply the required number for the long-term studies
•	Observations—growth, food consumption, general appearance
and behavior, mortality, organ weights, clinical laboratory
tests (blood, urine, organ function, enzymatic and metabolic)
and gross and microscopic examinations
•	In the case of organo-phosphorous and carbamate pesticides
cholinesterase inhibition and demyelinatlon studies were
to be made
Long-Term Toxicity (chronic toxicity)
•	At least two species, one a non-rodent
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•	Duration usually two years
•	Tests and observations similar to those above £or short-term
toxicity
Biochemical Data
•	Data from at least two species of animals
•	Observations: absorption, distribution, metabolic trans-
portation, elimination, possible accumulation, and the
effect of enzymes which should be examined because of the
nature of the chemical under study
•	Information on metabolism of pesticides and their other
conversion products in treated plants
Reproduction Studies
•	At least one specie, preferably two
•	At least two dosage levels, plus a control group
•	Usually three successive generations in the rat; two
generations are satisfactory If the results are conclusive
•	Preferably two litters per generation
•	Both the males and females should be treated for 60 days
prior to breeding; the second and third generations were
to be treated from weaning throughout the breeding period
•	Observations: fertility, length of generation, live
births, still births, survival at 4 days and at weaning,
sex of newborn and of weanlings, body weights, gross
abnormalties, and microscopic and skeletal examination of
young in last generation
Data on Man
•	From industrial exposure
•	From accidental poisoning and suicides
•	From controlled requirements In special cases
•	Useful biochemical data of the type indicated above
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Any additional studies that might be indicated by results of
the studies above.
When the FDA established a tolerance, and the USDA requirements were
met, a registration based upon the tolerance or no residue status was
granted. Additional data was required for each use (crop or pest) that
was indicated on the label.
Although the general requirements for registration were similar for
all pesticides, amount of data required and the complexity of tests and
results varied with the pesticide, its properties, and its proposed use.
Frequently additional data were required as the Initial tests were reported
to USDA and suggested the need for more or confirmatory information.
c. Experimental Use Permits
Another important feature of F1FRA which affected research and
development activities was the temporary permit program. Although FIFRA
originally provided no explicit authority to regulate the experimental
uses of pesticides, Section 7(a)(4) of the law provided the basis for
subsequent regulations. Section 40 CFR 162.17 (amended 1964), provided
for "temporary permits, not to exceed one-year period, for shipment of
limited amounts of a product which is to be tested, usually on a larger
scale, to determine its limitations." Permits were to be issued only for
bonafide experimental programs under supervision of qualified persons.
Permits were not required for substances that were being tested "only to
determine their value for economic poison purposes, or to determine
toxicity or other properties, where the user does not expect to receive
any benefit in pest control from its use." Also an economic poison for
experimental use by or under supervision of authorized federal or state
agencies did not require a permit. Both general (multiple shipment over
time) and specific (specific shipment and date) permits were Issued. If
tests were to be conducted so that residues could result on food or in
feed, one of the following were required: data were required to show that
no residue would be present, a tolerance or exemption from tolerance
(permanent or temporary) had to be established by the FDA and data pro-
vided to show that the experimental use would not result in residues which
exceed tolerances, or the food or feed derived from the experimental
program had to be destroyed, fed to laboratory animals only, or otherwise
safely disposed of. The permit application required certification of use
of the food or feed, shipping information, composition, quantities, data
on toxicity, description of the experimental program, percent of material
supplied without charge and proposed labeling information. Quantities
shipped could be limited and reports on the experimental program were re-
quired every three months. Experimental permits could be cancelled for
violation or for the protection of the public. As a result of the Imple-
mentation of this regulation, experimental permits could be easily and
readily obtained and potential pesticides tested broadly on an experimental
basis to gain research and development and marketing information for
industry. Many R&D activities were under the direction of state and federal
agencies (agricultural extension programs at universities) and no permits
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were required.
2. Changes to FIFRA
As Indicated earlier, the data requirements of FIFRA evolved over
the years from 1947 to 1971 at a slow but steady pace. Several major
changes occurred which significantly affected the research activities
of industry. Prior to 1966, pesticides could be registered with either
a "negligible residue" or with a "zero tolerance" as provided for in the
Federal Food, Drug and Cosmetics Act-, Section 346a. As a result of
advances in analytical techniques, and the growing realization that even
small quantities of pesticide residues could have important health effects,
a policy change was instituted in April 1966 that required re-evaluation
and reregistration of pesticides with zero tolerance or no residues,
and a finite tolerance was required for future registrations. USDA and
FDA agreed that then current registrations should be discontinued after
December 31, 1967 unless producers presented evidence to support a
finite tolerance or to show that progress was being made on work leading
to such evidence. Products which were being reregistered (every 5 years
under FIFRA) required additional data to support these new tolerance
requirements. It was the Intent that no pesticide registered after
January 1971 would have a zero tolerance or no residue as the basis for
registration. As discussed later, this change led to additional research
and development to assure continuation of registration of existing products
as well as to obtain registration of new pesticides.
A second major change occurred as a result of PR Notice 70-15,
June 23, 1970, in which the Dept. of Agriculture posed the following
basic questions to be answered in support of registration of pesticides.
•	What is the rate of dissipation of the pesticide in the soil?
•	What is the mechanism of degradation of the pesticide residues?
•	Do the residues leach through the soil?
•	Are the residues moved from the site of application by
runoff water?
0 Is the pesticide bound in soils, that is, are residues present
that are not readily extractable?
•	What levels of the parent compound and principal metabolites
will accumulate in fish, rabbit, and bird tissue and what
dosage related symptoms are exhibited during the laboratory
test period?
The data and studies required to answer some of these questions varied
with the compound, its proposed use, toxicity, and the details of the
registration review process at the time the application was submitted.
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A third factor which influenced the research and development
activities related to FIFRA was the Delaney Amendment to the Food, Drug
and Cosmetic Act (Title 21, Section 348(c)(3)(A), October 1962), which
effectively prohibited the existence of pesticides or their residues in
any measurable quantities on food if the pesticide or residue was a
known carcinogen. Additional test efforts were required (described
earlier) to determine the carcinogenicity of pesticides and their meta-
bolic products.
3. FEPCA
The FEPCA, or frequently referred to as "FIFRA, as amended," contains
many new provisions and is in the process of being implemented in the
period from 1972 to 1976. Only a portion of the expected regulations
and policies under FEPCA have been proposed or promulgated and the impacts
of the anticipated regulations are unclear. Nevertheless, there are
changes in the law which may impact R&D activities.
The registration requirements under FEPCA are very similar to
those under FIFRA. However, one major difference is that all pesticides
shipped, sold, delivered and received, both inter- and intra-state, must
be registered unless it constitutes an internal shipment from one register-
ed establishment to another operated by the same producer for packaging
or as a constituent of another product, or unless it is covered by an
experimental use permit. Another difference is included in Section
3(c)(1)(D) which requires that the Administrator may not consider the
test data supporting one application in support of another application
for registration, unless the second applicant has first offered to pay
reasonable compensation for test data and that the teat data is not pro-
tected from disclosure (e.g., information designated as trade secrets).
If the parties cannot agree on an amount and method of payment, the
Administrator shall make that determination, with an appeal procedure
specified.
Guidelines specifying the kinds of Information required In support
of registration are to be published and revised from time to time. At
present, several draft versions of these guidelines have been informally
issued. Most of the data requirements are similar to the latter stages
of FIFRA. Some additional requirements are being added as part of the
evolutionary process of learning more about the environmental and health
effects of pesticides.
The Administrator is to review the data Jn the application as expedi-
tiously as possible and either register the product or notify the
applicant that registration is denied. After receipt of the application
and the required data for a pesticide with a new active ingredient or
a changed use pattern, a notice of application must be published in the
Federal Register providing for 30 days for any federal agency or interest-
ed person to comment. The pesticide shall be registered if:
• its composition is such to warrant the proposed claims,
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•	its labeling complies with the requirements,
•	it will perform its intended function without unreasonable
adverse effects on the environment, and
•	when used in accordance with widespread and commonly recognized
practice it will not generally cause unreasonable adverse
effects on the environment.
The law specifically states that the Administrator shall not make any
lack of essentiality a criterion for denying registration and indicates
that when two pesticides meet the requirements above, one should not be
registered in preference to another.
Registered pesticides will be classified as either for general use,
restricted use, or both, with specific directions and clearly distinguish-
able packaging and labeling for general and restricted uses. A pesticide
will be classified for general use if it will not generally cause un-
reasonable adverse effects on the environment. A pesticide will be
classified as restricted because of its potential for harm to the applicator
or unreasonable adverse effects on the environment. If a pesticide is
designated restricted because of hazards related to acute dermal or in-
halation toxicity, the pesticide may only be applied by or under the
supervision of a certified applicator. (Applicators are certified by
states under plans approved by the Administrator, according to standards
for certification prescribed by the Administrator. These standards are
to be issued by October 1975.) If a pesticide is classified as restricted
because of possible unreasonable adverse effects on the environment, it
can only be applied by or under the supervision of a certified applicator
and may be subject to other restrictions by regulation (with an appropriate
appeals procedure). The classification of a pesticide may be changed
with the accompanying notification of the registrant and publication in
the Federal Register. If the Administrator denies registration of a
pesticide, the denial and reasons therefore must be provided to the
applicant and published in the Federal Register.
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Section 5 of FEPCA calls for application and issuance of experi-
mental use permits to allow the applicant to obtain information necessary
for registration of a pesticide. A temporary tolerance level is to be
established (if required) before Issuing an experimental use permit;
studies may be required to detect whether a new pesticide may cause un-
reasonable adverse effects on the environment when used under an experi-
mental permit; experimental use permits can be revoked by the Administrator,
and the Administrator may authorize states to issue an experimental use
permit for a pesticide.
Several new provisions for cancellation, change In classification,
and/or suspension of the registration of a pesticide or hearings to
determine a course of action are provided for in the law. These processes
are to occur if: the registrant does not request continuation of the
registration after a five-year period; if the pesticide or its labeling
does not comply with the provisions of the Act; if the use of the pesti-
cide in accordance with widespread and commonly used practice generally
causes unreasonable adverse effects on the environment. Hearings,
emergency orders, public heatings, scientific review and judicial review
are also delineated.
The law calls for registration of establishments in which pesticides
are produced and submittal of data on the types and amounts of pesticides
produced.
As under FIFRA, books and records of pesticide production operations
movement and shipment are to be kept and made available to EPA staff
designated by the Administrator. FEPCA contains a number of new provisions
which enhance the federal enforcement capability. Both civil and criminal
penalties are authorised. Authorized representatives of the Administrator
may enter pesticide establishments or other location of storage or sale
of pesticides for the purposes of inspection or sampling, after giving
appropriate reasons for the inspection. A number of new unlawful acts
were added to FIFRA, Including the use of any registered pesticide in a
manner inconsistent with its labeling. Stop sale, use or removal orders
are authorized, and products in violation of the Act may be seized.
The administrative and judicial review procedures are clarified,
and restrictions to pesticide Imports and exports (similar to FIFRA)
are provided.
Several other Important points of the law (with regards to possible
impact on R&D) include the provision for indemnity payment to certain
persons who suffered losses by reason of suspension or cancellation of
a registration. The Administrator is to establish procedures and regula-
tions for the disposal or storage of pesticide packages and containers,
and to establish packaging standards. The Administrator also shall
undertake research as necessary for the purposes of carrying out the
Act, and give priority to research to develop biologically integrated
alternatives for pest control. Under Section 24, a state may provide
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registration for pesticides formulated for use within its bounds, if
it has been certified by the Administrator to do so.
As with FIFRA, the implementation of FEPCA will evolve as new
regulations are promulgated, with a schedule which extends through 1976.
Guidelines for data requirements for registration have been drafted and
may soon be Issued. Criteria for classification of pesticides have been
drafted and announced recently. Regulations for registration of pesticide-
producing establishments, submission of reports, and labeling were issued
in November 1973. An interim policy for the administration of Section
3(c)(1)(D) was issued in November 1973. Proposed regulations to establish
standards of competence for applicators of pesticides were Issued in
February 1974. Revised proposed procedures for the use of pesticides
for experimental purposes were issued In March 1974. Many of these
recent proposed regulations are now receiving comment from the public
prior to their promulgation.
4. Comparison of FIFRA and FEPCA
It is not appropriate to compare FIFRA and FEPCA on a section by
section basis because FIFRA evolved over a 25-year period and many of
the anticipated regulations and guidelines under FEPCA have not yet been
issued. Further, many of the regulations and provisions concern admin-
istrative processes and have only a secondary Impact on R&D activities,
if any. In this section we will present a brief time analysis of portions
of FIFRA, showing major changes, and then compare the principal features
of FIFRA and FEPCA which may influence R&D activities.
Table 8 shows the evolution of the principal regulatory actions and
policies and the changes in data required (primarily for registration)
over the 25-year period after passage of FIFRA. The exact dates for the
implementation of the regulations and policies is generally unimportant
since the Impacts caused by the changes in regulations and data require-
ments have been gradual.
The most significant changes in FIFRA, as determined from our
discussions with industry, were the change in residue data requirements,
addition of environmental data requirements and overall continued requests
for more precise and extensive health and environmental data.
Table 9 compares the principal features of FIFRA (at a time just
prior to FEPCA) which affect R&D activities with similar features of
FEPCA (at the present).
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1947	1952	1957	1962	1967	1972
Lav
Enactment of FIFRA
Amendments to FIFRA
Delaney Amendment
to Food, Drug and
Cosmetic Act

FEPCA

Regula-
tions
Development of
Regulations and
Their Imple-
mentation
Amendments, Changes
and Interpretation
of Regulations

PR 70-15
Requirements
for Environ-
mental Data
Regulations for
Implementation
of FEPCA

Policies
Priority on
Efficacy and
Prevention
of False Claims
Priority on
Efficacy and In-
creasing Importance
on Human Safety
Environmental
Priorities
Increasing
Priority on
Assuring No Un-
reasonable Adverse
Environmental-
Effects (Including
health)

Data
Require-
ments
Modest Data Re-
quirements Under
Initial Imple-
mentation
Increasing Require-
ments for Toxicity
and Efficacy Data
Added Carcino-
genesis Data
Requirements
Changes in
Tolerance and
Residue Require-
ments
Added Environmental
Data Requirements
From PR 70-15,
e.g., variety of
species, bioaccumula-
tion, degradation
products, etc.
Admin-
istration
Jointly by USDA,
Administra-
Administrat ion
FDA, Dept. of 	
	> tion of FIFRA—>
of FEPCA by EPA
Interior with
Other Agency Comments
by EPA

TABLE 8. TIME FRAME FOR CHANGES IN FIFRA

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TABLE 9. BkXEF COMPARISON OF FIFRA AND FEPCA
FIFRA
FEPCA
Administration
USDA, FDA and Dept. of Interior
from 1947-1970; EPA from 1970
EPA with input from other agencies
Registration Requirements
Applicability
Pesticides in interstate
commerce. Pesticides "for
experimental use only"
excluded.
Pesticides in inter- and intra-
state commerce. Pesticides "for
experimental use only" excluded.
Procedures
Statement to be filed
with name of pesticide and
applicant, labeling includ-
ing claim and directions for
use, description of tests and
results, if requested.
Statement to be filed with name of
pesticide and applicant, proposed
labeling, including claims and
directions for use, formula, descrip-
tion of test and results, if requested,
offer to compensate for use of data,
request for general or restricted
use classification.
Data Required
Toxicity and efficacy data in-
cluding residues and metabolites
with early emphasis on human
health and product performance;
environmental data added later,
generally increasing requirements
with time, data requirements
vary with product and proposed use.
Generally similar data to FIFRA just
before FEPCA with some further in-
creases; apparently some unspecified
requirements, guidelines not
completed, data requirements vary
with product.
Approval of Registration
Approval granted if tolerance
established by FDA (if needed)
and USDA requirements met.
Approval granted if composition
warrants claims, meets requirements
of Act, will perform intended function
without unreasonable adverse effects
on the environment, in normal use
will not generally cause unreasonable
adverse effects on the environment.
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FIFRA	FEPCA
Cancellation of Registration
Suspension or cancellation
procedures when pesticide is
in violation of the Act with
appropriate review appeal
process. Cancellation after
5 years unless continuation
requested by registrant.
Similar, but somewhat stronger,
suspension and cancellation pro-
cedures, including stop sale, seizure,
emergency order, etc., provisions.
Public hearings, scientific review
and appeal process. Cancellation after
5 years unless continuation requested.
Classification of Pesticides
No classification under FIFRA.
Classification of pesticides as
general use, restricted use, or
both. Changes in classification
provisions.
Certified Applicators
Not required under FIFRA.	Restricted use pesticides to be
applied by certified applicators
only; applicators to be certified
by states in accordance with
standards set by Administrator.
Books and Records
Records of delivery, movement
of pesticide, etc., to be
provided to authorized person
on request.
Use of
Similar to FIFRA with additional
requirements for registration of
establishments which produce
pesticides and data submittal.
Data
Administrator not constrained	Applicant must agree to pay reasonable
from using efficacy or effects	compensation if others' test data
data from previous applica-	are used in support of registration
tions as basis for acting on	application. Provisions for protec-
other applications. No	tion of trade secrets in law.
compensation for use of data.
Unlawful Acts, Enforcement and Penalties
Specification of unlawful
acts, provisions for en-
forcement, including sample
collecting, etc., and
assessment of criminal penalties.
Similar unlawful acts strengthened
enforcement provisions, including
civil and criminal penalties, sampling
and inspection and prohibiting use
of pesticide except as specified on
label.
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FIFRA
FEPCA
Experimental Uae Permits
Required for experimental
use of non-registered
pesticides except under
supervision of federal and
state authorities.
Temporary tolerance may
be needed. Modest toxicity
data needed. Quantities
limited, reports required,
general retail sale prohibited.
Required for all experimental use
of non-registered pesticides,
temporary tolerance may be required.
Increased data requirements for
permit. States may issue experi-
mental permits, if authorized,
limitations on acreage resale pro-
hibited, Increased notification
and records of shipment and use,
etc.
Storage, Disposal and Packaging
Pesticides subject to
packaging standards set
by HEW under Poison
Prevention Act.
Administrator to establish procedures
and regulation for storage and
disposal of pesticides and containers.
Administrator to set packaging
standards to protect persons from
serious illness.
State Functions
Responsibility for manu-
facture and use solely
within state.
May regulate sale or use within
state; shall not impose additional
or different labeling or packaging
requirements; may provide fjor registra-
tion of pesticides for distribution
and use within state for local needs
if certified by Administrator;
certify applicators according to
federal standards.
Indemnity
No provisions.
Indemnification for certain persons
suffering loss as a result of
suspension and cancellation of
registration.
Research
No specific research
provisions.
Administrator to conduct research
to aid in implementation of Act
with priority on biological controls.
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C. SPECIFIC IMPACTS OF LEGISLATIVE AND REGULATORY ACTION
1.	Introduction
The changes which have occurred in the research and development
activities of the pesticide industry in the past 25 years can be attributed
to many factors—new agricultural policies, development and improvement
of farming methods, changes in the general economy, development of inter-
national markets and balance of trade considerations, farm labor supply
and demand, technological advances, environmental awareness of the public,
attitudes toward public health and safety, availability of raw materials
for organic synthesis and federal and state regulatory actions. The
relationships among these factors are complex; there have been many factors
which act in concert to bring about a new direction or trend in research
such as the specialization in research on herbicides by a particular
organization or the initiation of a biological control research program.
The trends in research and development activities have been described
in Section III. Here we will attempt to identify and describe the impacts
of specific regulatory actions on pesticide research and development
activities. In Section D we will relate general trends and changes in
research and development activities to combinations of regulatory actions
and other factors not directly influenced by pesticide laws or regulations.
The format used for this section will be to state the specific impact
or general change noted and then discuss the reasons for the impacts and
other possible alternative views. The impacts, reasons, and alternative
views are based primarily upon information and data provided to us in
discussions with industry under this contract, and secondarily on publish-
ed information and our own interpretation of the research and development
activities and market structural elements of the pesticide industry.
2.	Data Required for Pesticide Registration
The steadily increasing requirements for data, on hexilth, safety and
enviAonmentaZ z^ects oft pesticides in order to obtain registration have
significantly increased the cost and time frame ion peAticide fieQiAtrui-
tion and development by industry and have r.eAuJLted in a decrease in the
growth rate of innovative research and development activity. These costs
and delays axe balanced by the greater understanding of pesticide ejects,
derived fr.om the registration data, and by the registration of elective,
safe and environmentally sound pesticides.
When FIFRA was first enacted, the principal emphasis in the required
data was to demonstrate the efficacy of the pesticide. As the use of
pesticides became more widespread and as the public became more informed
on health effects, steady increases in the data required for registration
occurred. Toxicity testing became more important; more data were required
to substantiate claims of efficacy, lack of damage to food crops, and
lack of residues on food and in the soil. The duration of required tests
was increased, and as analysis methods became more sensitive and sophisticated,
70

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the requirements for more accurate and precise measurements of toxicity,
residues, metabolites, etc., were increased. The era in which the
registrant could "walk the application through the registration process"
came to a close. Data requirements under FIFRA were provided by USDA to
applicants, however changes in requirements were frequent, and the
quantity of data required increased as knowledge of health and environ-
mental effects improved. Although general data requirements were the
same for all pesticide applications, there was considerable flexibility on
the part of the USDA reviewers to ask for more or less data depending upon
the type of compound and the past experience with related compounds.
Communication channels between Industry and the regulatory agencies could
be described as good, and industry generally felt that USDA was an ally
to the producer as well as a regulator.
According to industry, a significant Impact on data requirements
resulted from the policy change in 1966-1967 which called for more extensive
and sensitive residue data when pesticides were registered or reregistered.
Several companies reported to us that "from 1967 to 1970 we essentially
shut down our innovative research to obtain the required safety data."
Other companies acknowledge the change, but indicate that it was not un-
reasonable, and "would have come along anyway" as a result of increased
health concern as well as because of Improvements in analytical methods.
Data requirements continued to increase, with the next major impact result-
ing from PR 70-15 which added significant new data on environmental impact
and the fate of pesticides in the environment. Some pesticide companies
believe that the shift in emphasis from efficacy and human health to en-
vironmental concern represented the greatest change in data requirements
and the greatest Impact on cost and timing of the registration process.
The reasons given include the "new type of data required, the development
of new analytical methods, needs for tracer studies, different type of
staff required, larger dimensions of the animal studies, sequential requests
for additional environmental data, etc."
Another important factor mentioned by several companies was the gradual
increase in data required to show definitely the absence of health effects
such as carcinogenicity, mutagenicity, teratogenicity, etc. Some
industrial sources attribute the major increase to the Delaney Amendment,
others to public pressure and federal response in terms of data required
for registration. The principal Impact of the tests needed to obtain
these data was not primarily the added cost, but the time required to
conduct the studies. The two-year period for carcinogenicity tests
lengthened the overall process of development, even though most companies
conduct this work at the same time as'they are doing other studies of
similar long duration. Industry considers the two-year duration as almost
a three-year test period, when planning, analysis, reporting of the results
are included.
Although the guidelines for data in support of registration under
FEPCA have not been formally issued, drafts of the guidelines have been
circulated both within and outside EPA to industry. From discussions with
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Industry staff who have reviewed these guidelines, we conclude that there
are few major changes in types of data required for registration under
FEPCA, but that the quantity of information needed continues to grow as
before. This continued increase requires additional R&D efforts and can
detract from more Innovative development of new and better pesticideB.
In our discussions with industry, we were provided with many examples
of the impacts—delays and costs—to industry which were attributed to
data requirements for registration. Most of the comments, and complaints,
were based upon histories of registration of specific products, or
particular problems which each specific company encountered. In the next
few paragraphs, we will generalize these specific comments and report
those suggestions of industry in terms of data requirements and accompany-
ing registration procedures.
Industry's views of the data requirements for the registration process
fall in two categories—technical considerations, including the relevancy,
significance, methodology and necessity of various tests—and procedural
considerations. Most companies agree that the technical aspects of the
tests and required data are costly, time-consuming, and detract from
other areas of R&D. However, they also agree that, for the most part, -
these tests and data are necessary to provide scientific basis for	\
registration of pesticides to assure health and safety to man and the
environment. A frequent comment of industry is: "many or most of the
tests required by EPA must be conducted by industry in product development
(even in the absence of regulatory action) to assure that the product can
be successfully marketed and to insure that the product is safe, i.e.,
protect the company from possible litigation." Industry, on the other
hand, feels that all tests required for registration need not necessarily
be conducted on all products and that better use should be made of past
data from similar tests with the same or related products on similar or
related crops. Industry questions the necessity and relevancy of some of
the questions asked by EPA reviewers in the reviews of registration applica-
tions, particularly those questions which relate to the fate of the
pesticide in the environment, analysis and tracing of decomposition
products. The tests in this area of study are some of the most costly
and time-consuming, and the results can vary considerably depending upon
environmental conditions. Furthermore, the tests require the development
of new, sensitive analytical methods, and multiple test areas.
A problem exists in that, on one hand, industry would like to see
test requirements made specific and relevant to particular products and
crop or insect usages, i.e., leading to flexibility in test requirements
among products. On the other hand, a portion of industry would like to
have the data requirements for all products and usages carefully defined
so that they "know how to proceed" and could thus count on a more
straightforward registration process. Clearly a compromise must be
accepted in which certain requirements must be identified for all products
and others must be dependent upon the product, use, and judgment of
the EPA reviewers.

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Other, more specific technical problems noted by industry in the data
required for registration which have added to the cost and time of
pesticides R&D include:
•	Requirements for the development of new analytical techniques;
•	Increased numbers of species for animal tests, including some
which are difficult to use;
•	Breadth and possible duplication of tests needed for mixtures
of pesticides;
•	Accuracy requirements for product content in low strength product
formulations;
•	Difficulty in conducting tests on aquatic herbicides; and ,
•	Possible requirements to use ASTM specified test methods which
may not be the most desirable or cost effective for particular
products or research facilities.
Despite these technical problems, industry generally recognizes the
inevitability that the data required for pesticide registration will
continue to increase and that industry is competent and capable of dealing
with the technology.
The procedural aspects of the registration process also affect the
data requirements and thus have an impact on R&D. In fact, the procedural
aspects of the registration process generally draw more criticism and
concern from industry than the technical aspects, although it is difficult
to determine whether the impacts on R&D are greater because of technical
or procedural problems. The "absence of definitive registration guide-
lines," "inconsistent and serial data demands at the discretion of the
individual reviewer,""lack of communication between applicant and reviewer
and lack of disclosure to Industry of changes in data requirements,"
"delays in the review process by EPA" are typical of industry comments.
The principal impact of these problems on R&D include:
•	Increased time required for the registration process;
•	Increased staff needed to meet and handle procedural
requirements;
•	The diversion of R&D efforts away from the discovery and
initial development of other new compounds;
•	The cost of the added data; and
•	The loss of income both in the near-term because of delays in
product sales and in the long-term because of the reduction
of time in which the company has a proprietary position.
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Fran our discussions with Industry and EPA, some of the comments
seem to be justified but may be caused by the lack of EPA staff in the
registration (and criteria and evaluation) areas needed to process the
increased amount of work. Many of the procedural problems will be
resolved in time with the acquisition of EPA staff, with the issuance of
registration guidelines with reasonable provisions for changes and informa-
tion flow to current applicants, with the successful implementation of
the product manager program at EPA, and with the resolution of problems
related to regulations and guidelines in other areas related to data—
experimental permits, 3(c)(1)(D), etc.
Concerning the impact of registration data requirements on R&D
activities in biological control methods, there is some disagreement
among the few industrial proponents of biological controls. One faction
suggests that biological control approaches have been "separated" from
others in terms of data requirements in the registration and review
process and should not be; such separation leads to a greater degree of
caution by EPA and further data demands. Others question the validity
of some of the required tests, indicating that they are too extensive in
view of the specificity of the compounds considered. Guidelines for
registration with specific considerations and interpretations for those
biological approaches that are very different from traditional chemical
approaches are needed. There are sufficient technical problems in the
development, storage, application, and use of biological control methods
which occupy the efforts of industrial R&D, so that there are only few
compounds or approaches at the registration stage where they can be
significantly impacted by EPA data requirements. For these few, however,
procedural problems in EPA are probably more significant than technical
problems.
There are several other types of positive and negative impacts of
the data requirements for registration on industry." As a result of the
test requirements, the research process in industry has been streamlined
and made more efficient in certain areas. Earlier decisions are being
made on whether to pursue specific compounds, and the screening processes
have become more effective. Pesticide research groups have tended to
specialize in certain areas, and to use outside contractor help in others.
Typically, even major pesticide research organizations will have toxicity
tests, bioconcentration studies, metabolism studies, carcinogenicity,
teratogenicity tests, etc., done under contract with research laboratories
that specialize in these areas. This is often done in order to reduce
costs and maintain staff levels yet retain control over critical areas in
the R&D process that are efficacy, field test or marketing oriented.
Some companies have begun to contract some of the screening operations
as well. As a result of the added data requirements for registration,
much more information is available on the behavior and fate of pesticides
in the environment at early stage, which hopefully can be utilized to
prevent long-term adverse environmental effects.
The potential impacts of increased data requirements for registration,
described above, are based upon industry's initial views of how Section 3
of FEPCA would be implemented. After data were collected for this report
(Spring 1974), additional and far-reaching regulations and guidelines have
been developed and/or Issued by EPA pertaining to registration requirements
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and classification of pesticides. These guidelines and regulations could
have additional potential impacts which are not addressed here.
3. Experimental Use Permit System
The ionopoAed experimental ut>e permit AyAtem mil incnea6e co&t&,
timing and tiiskb in peAtijdde Ket>ejxnc.h and development activities.
InduA&ty mil challenge the pnxipo&ed i^ulationt* unlet>4> a method ii> iound
to obtain the nece&&any cue and marketing data.
a. Permits Under FIFRA
FIFRA provided a basis for the issuance of permits for shipment of
pesticides. The temporary permit system under FIFRA. is described under
paragraph 362.17 of Title 7, Ch. Ill, Regulations for Enforcement of
FIFRA. The principal features of the system were:
•	Permits issued for one year for shipments of products in limited
amounts for bonafide experimental programs only;
•	Purpose of permit was to authorize tests to determine pesticide
limitations;
•	Information and data on products and test programs necessary
to protect the public may be required to be submitted;
•	Permits were not required if the test purposes were only to
determine the value as an economic poison, or to determine
toxicity or other properties and were of no benefit in pest
control to the user;
•	The pesticide could not be offered for general retail sale;
•	Permits were not required for experimental use of pesticides
under the direction of federal or state agencies;
•	A tolerance, exemption from tolerance, or temporary tolerance
or temporary exemption was necessary if the pesticide may cause
residues in or on food or feed or if the food or feed derived
from the program was not destroyed or disposed of in a manner
which protects the public;
•	Data required with the permit application included: statement
of nature of the program, states and geographic areas used,
previous test results, proposed labeling, amount supplied without
charge, approximate quantity and dates or time period of shipment,
data on toxicity, etc.;
•	The quantities of the pesticides covered by the permit could
be limited if information or effectiveness or hazards were in-
sufficient to justify the scope of the work;
•	Reports were required on a three-month basis.
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The temporary permit system was used widely by commercial pesticide
developers for several reasons:
•	To obtain data on efficacy, application rates and methods,
effects of environmental and geographic variables;
•	To provide a means for obtaining data for registration—
environmental fate, residues, decomposition, behavior of
pesticides in the soil;
•	To obtain marketing information—acceptance by farmer,
distributor, user information, comparison With competitive
products.
The information gained from the experimental field tests was integrated
by the commercial developers into a decision-making process which resulted
in stopping research and development on certain compounds and the continu-
ing or accelerating research and development of others. Industry concensus
is that only one or two compounds out of ten used in extensive field
studies went into full Scale development.
Several modes of operation were employed in the temporary permit
system. Many companies operated their own farms over which they had
complete control of the food or feed derived from the experimental program
or had long-term leases on land used for experimental purposes. Others
used distributors, formulators, food companies or independent farmers to
manage and conduct the field work on their own farms and report the results
of the programs to the pesticide developers. Still other pesticide
developers would contract field test work to independent farmers, in
addition to, or instead of the use of their own farms. There was extensive
cooperative effort with universities, state colleges, and state and
federal agencies for field testing. This latter work did not require the
temporary permit and provided the opportunity to obtain data in other
locations and on other crops or insects for use in registration applica-
tions. This system provided considerable flexibility for the commercial
developers in several ways:
•	They could obtain both market and performance data to assess
the effectiveness and marketability of the compound in
different climatological and weather conditions in various
parts of the country;
•	They were not necessarily committed to the operation of
their own farms with the attendant capital and operating
costs; and
•	They could relatively easily follow the insect or weed problems
in various locations.
The system was believed to build distributor loyalty as well as prepare
the distributor for ultimate sale of the product. Initial contact with
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the farmer through the distributor—one of the main determinants of market
practices—was felt to be essential to determine the potential for the
various compounds. The data required for the experimental permit were
relatively modest, at least compared to full registration. The time
required to get a permit application approved was between about 3 to 6
months, if sufficient work had been done to obtain a temporary tolerance
(if necessary). The pesticide developers and the regulatory agencies all
recognized the need for the field test portion of the pesticide develop-
ment process; the temporary permit program provided some measure of control
to insure that the health and welfare of the public were not being
compromised by the testing programs under the permit system.
The relative "looseness" of the regulations, and the ambiguity of
some of the terms and provisions, was in part responsible for indiscre-
tions and violations on the part of several pesticide developers. In
some cases, relatively large quantities of "experimental use" pesticides
were sold, and indeed the user obtained considerable benefit in pest
control while the developer was obtaining market and efficacy data. Despite
the occasional high volume sale of specific experimental pesticides by
some companies, much profit could not have been realized by these companies
because of the relatively high unit price of the pesticide at this stage
of development compared to the price at final full production. Neverthe-
less, any income was welcomed by industry to offset the development cost.
b. Permits Under FEPCA
With the passage of FEPCA, the emphasiB in the experimental use
permit system seems to have shifted from efficacy and safety to environ-
mental impact. Section 5 of FEPCA provides that any person may apply for
an experimental use permit for a pesticide and that the Administrator
may issue one to allow the applicant to accumulate information necessary
for pesticide registration. The requirements for temporary tolerance
is similar to that under FIFRA. Additionally, the law specifies that
studies may be required to determine whether the pesticide used under
the permit may cause unreasonable adverse effects on the environment,
that experimental permits can be revoked, and that the states may issue
experimental permits if authorized.
The proposed regulations for experimental use permits under FEPCA
(Fed. Reg. Vol. 39, No. 60, March 27, 1974) represented a substantial
departure from previous regulations. Since the publication of the proposed
regulations, comments have been provided by interested parties to EPA,
and the proposed regulations are under review. In this report, we do
not feel it is appropriate for us to comment on the legality, wording,
emphasis, or reasonableness of the proposed regulations, but rather to:
(1) identify the principal changes in the regulation, (2) summarize some
of industry's objections to these changes, (3) provide information on
industry's views of the likely impacts on R&D if the regulations are
promulgated and implemented as originally proposed, (4) present our views
of possible Impacts, and (5) make several recommendations or suggest
possible alternative methods of implementation.
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c. Changes In the Regulations
The principal changes or new regulations with regard to experimental
permits as proposed under FEPCA are:
•	Pesticides may be sold and distributed only to participants
involved in the experimental program and are not for resale
or other retail sale or other distribution.
•	Exceptions to the permit system include pesticides used in
screening tests in which the only purpose is to determine
if they have value for specific pesticidal purposes and from
which the user does not intend to receive any benefit from
pest control from their use. These tests are limited to
laboratory and small plot replicated field tests less than
10 acres by federal or state agencies, universities or
commercial developers on areas leased or owned by them and
continually operated as an experimental farm on a long-term
basis, where the crop or test subject is destroyed or
suitably disposed of.
•	The permit application calls for: detailed description of
the proposed test program, the crops, fauna, flora, sites,
modes and situations of pesticide application, number of
acres for test, name and address, etc., of the person
responsible for day-to-day administration of the program
as well as the participants in the program.
•	The data required for the application include: composition
of formulation by name and weight, chemical and physical
properties for each ingredient including manufacturing
processes and analytical methods, rates of decline of residues
on the treated crop or environmental site. Biological data
are required including the description and results of known
testing to determine toxicity and effects on species at the
site of application, adverse effects to non-target species,
and adverse effects on the environment. Toxicity tests and
data relevant to users and other exposed persons must be
provided.
•	Those awarded permits must supervise the test program, evaluate
the results and report immediately any adverse effects.
•	Provisions for entry of authorized persons to the test area
for inspection and compliance are Included.
•	Labeling provisions are changed to include almost all informa-
tion required on permanent label.
•	Notification of shipment by applicant to the Administrator
must occur at the time of shipment including amount of each
shipment.
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•	Revocation procedures with provisions for hearings are
prescribed.
•	The regulations do not exclude federal and state agencies
from the requirements for an experimental permit.
•	Processing of permit applications will require at least 90
days.
d. Industry's Oblections
Industry has raised strong objections to the regulations as initially
proposed; most of these have been submitted in writing and are publicly
available. In our discussions with industry, we were informed by many
companies that the proposed experimental use permit program will have more
serious changes from FIFRA to FEPCA. The objectives were based on early
industry assumptions of how the tegulations pertaining to Section 5 would
be implemented. Since this time (Spring 1974) the proposed regulations
on the experimental use permit program have been reviewed at EPA; some of
the objections, summarized below, may have changed in light of the currently
proposed regulations. The principal objections run the gamut from pro-
cedural to operational, to technical (in terms of data requirements), to
philosophical.
The procedural objections include:
•	Anticipation that publication in the Federal Register of applica-
tions for permits will include disclosure of chemical, structure,
etc., resulting in premature disclosure of research efforts and
potential products.
•	Requirements for more complete labeling may be unnecessary,
only emergency information and warnings since this may again
disclose information prematurely.
•	Additional paperwork is involved, e.g., anticipated daily
reporting of shipments.
•	Inspection of field studies is desirable but needs to be
scheduled to avoid inconvenience to participating farmers.
•	Expectation that extensive cooperation with the states and
EPA regions will be required.
•	Minimum of 90 days review of application is expected to yield
scheduling and other problems since the experimental programs
must be conducted within limited seasonal time frames.
Operational objections include:
•	Exclusion of resale will prevent participation of distributors,
formulators and others from perdW.t programs and limit contacts
with farmers, etc.
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•	Requirements for small tests on owned or long-term lease
property for continual use as experimental farms are believed
by industry to be impractical, costly, and unnecessary.
•	Specification of the exact location of the test program may
not be appropriate, particularly for tests on certain pests.
•	Anticipation that state and federal agencies (and universities
and agricultural colleges) will need permits for most of their
work.
Technical objections include:
•	The data requirements for the permit are extensive and out of
proportion to the possible effects of the experimental use
(particularly if quantities are limited by the Administrator).
•	Toxicity data is felt to be appropriate, but environmental
requirements anticipated are unreasonable. (The common
complaint is that a "Catch 22" situation exists where the
experimental use permit is needed to do the tests required
to obtain the data for the permit application.)
Philosophical comments include:
•	There is very little difference between the requirements for
registration and for the experimental use permit under the
proposed experimental use permit regulations. Is this the
purpose and Intent of the permit program?
•	Is it appropriate to make special provisions for innovative
pest control methods and can this be done so that it is not
discriminatory?
•	The proposed regulations make it mandatory to go through the
experimental permit program in the process of developing a
pesticide. Is this necessary?
e. Potential Impacts of the Proposed Regulations
It is not possible to identify in quantitative terms the potential
impacts of the proposed experimental use permit program since this
depends on the final regulations promulgated and the implementation
procedures involved. Nevertheless, we can present, and comment on,
several anticipated impacts and some of industry's reactions in terms
of research and development activities.
•	Increased coat of R&D—the cost of the research and development
process will increase for several reasons. First, more
research will be required to obtain data necessary for the ex-
perimental use application. Although these data can ultimately
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be used In the registration application, only a portion of
pesticides which enter the experimental permit stage are
commercialized, so that the total expenditures for all compounds
(those which succeed and those which fail) will Increase.
Second, a larger number of research and development staff will
be needed to follow and manage the experimental permit program.
The unavailability of sites for the test program in various parts
of the country, through agricultural research facilities and
other organizations, will require that pesticide developers own
or lease more land for continued experimental purposes, or
spend more time obtaining cooperation from a greater number of
participants. One major company estimated that the cost of
additional land for experimental use will amount to more than
$2,000,000 and that this will allow them only to work on about
10 major crop species in their tests. There is anticipation
that the quantities of pesticides that can be sold under the
permit program will be greatly reduced because of resale prohibi-
tion and loss of use of contract farmers, etc. This will cut
back any return now provided to offset the R&D cost.
The increased R&D cost could result in several impacts: (1) the
cost will be passed along to the consumers of those pesticides
that are eventually registered and marketed, (2) the increased
experimental use permit costs will result in more emphasis on
other uses of registered products and decrease in innovative
research, (3) the number of new products reaching the market
will be decreased.
• Changes in timing of the R&D process—there are two principal
impacts on the timing of the R&D process that can result from
the implementation of the proposed experimental use permit
regulations: (1) Increase in overall length of the pesticide
development and registration process and (2) shifting the order
and scheduling of the R&D activities. Current industry experience
indicates that an average of 7 months may be required for obtain-
ing an experimental permit under present FIFRA requirements
(prior to recent proposed experimental permit regulations).
The duration depends upon what is considered as "obtaining the
permit," i.e., once the application for permit has been submitted,
it may take only 3 or 4 months to obtain EPA approval; if more
data are required by EPA or if obtaining original data is con-
sidered as part of the duration, then clearly the process can
require 6-18 months depending upon the level of detail of data
need with the application. This level is not clearly defined in
the proposed regulations, but is left to the discretion of the
reviewer and the Administrator by necessarily open ended clauses
in the regulations, e.g., "appropriate data on rate of decline of
residues on the treated crop," "such additional pertinent informa-
tion as the Administrator may require," etc. Although it may
require up to 2 years to obtain the experimental use permit, it
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does not follow that the registration and pesticide development
process will be increased by the same time because much, if not
all, of the data required for the permit may have to be obtained
eventually for full registration. The extension of the R&D and
registration process will probably result more from the administra-
tive and processing delays rather than from the added data
requirements. (As mentioned earlier, the costs will increase
because of the need to obtain toxicological and environmental
data in applications for experimental use permits for many
potential products and not only those few potential products
¦which have passed the field test program.) Industry's fear of
delays and lengthening of the time frame stems from the indica-
tions in the regulations that at least 90 days will be required
for review of the permit application. Also, past experience
indicates that the timing of the experimental use permit is
critical. A permit granted in September for product use on an
insect pest which is prevalent in June or July is of little value
to the developer since he must wait until the pest appears again.
Industry almost always expects to lose "a growing season" because
of the turnaround time in getting an experimental permit and in
making the necessary arrangements for the field program. There
should, however, be little additional delay because of this 90-
day review requirement.
A more important change in R&D activities may be the shift in
timing of parts of the process. The extensive toxicological,
environmental degradation, residue and metabolism studies have
in the past been done concurrently with, and sometimes after,
extended field studies which frequently came under the permit
system. Under the new regulations, as anticipated by industry,
the initial work in these areas will be required before an ex-
perimental use permit is approved. Thus developers will have
to make this initial investment earlier in the development process,
and the risks associated with these earlier expenditures must be
borne by industry.
f. Development of Market Data
A major benefit that the developers of pesticides receive from the
previous experimental use permit system is marketing information derived
from farmers, distributors and formulators aB well as from the managers
of their own field programs. Industry believes that the efficacy of the
pesticide, the acceptance of the pesticide by farmers and distributors,
and the advantages of the new pesticides compared to competitive products
are best evaluated in the field program. They feel that the sale of
the experimental product is beneficial, since it helps determine how
much farmers and others may be willing to pay for the product if it is
commercialized. (The actual cost of production of the pesticide at
this stage is usually high, but developers can adjust the sales price
to determine if they should plan to distribute the new pesticides.)
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They also obtain reactions from the farmers and gain knowledge and
experience with the product. The developers use the permit system to
enable them to contact more farmers indirectly through the distributors
and indirectly to obtain distributor loyalty. Marketing information is
needed from several parts of the country in order to make decisions as
to whether to continue to pursue a potential product, or to determine if
they should make the necessary capital investments for new production
facilities. Industry relies on these market data to distinguish between
"the compound that looked interesting" and "the one that could really
be made into a new product." Industry feels that the cost of the proposed
experimental use permit as well as the restrictions imposed will limit
the amount of marketing information that will be obtained in a practical
sense, and thus hamper the decision-making process in pesticide develop-
ment. This process could also result in a decrease in the number of new
compounds brought to the marketplace in any year because of the hesitancy
of industry to go ahead when a product performance or its acceptance is
not as well known as it has been in the past.
r. Small Companies/Large Companies
It is the general concensus of industry that the proposed experimental
use permit system will have more of an impact on the small pesticide
companies than the larger companies. This is because the smaller companies
presently rely more on the agricultural research services and state or
federal facilities than large companies. Many of the smaller companies
have only one experimental farm and cannot afford to enter into long-
term leases for large test areas or purchase farms in several parts of
the country. The smaller companies frequently rely on distributors or
dealers to assist in the test program and feel this will not be possible
with the proposed resale provisions of the regulations. Generally, the
larger companies have several research farms or large leased areas in
which they can test under the permit system. Further, they are more
willing to make the large capital investments needed to keep up these
properties for experimental use. Where possible, we expect large companies
to use their own experimental farms for the field work necessary to obtain
registration data.
h. Biological Controls
The discussion in the Federal Register preceding the proposed
regulations on experimental permits suggests that special procedures or
information requirements be provided for experimental permits on innovative
pest control methods. Certainly those developers of biological controls
would welcome changes to eliminate what they believe are unnecessary tests
or inapplicable data requirements. Further, it is generally accepted that
many biological control approaches need larger test areas than other
pesticides. Those not developing biological controls are opposed to giv-
ing special consideration to any group of compounds. Since they feel
little is known about biological controls, such approaches should be
carefully examined. The most tenable solution is a careful review pro-
cedure by EPA staff experienced in biological control approaches to
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determine the extent of data required before a permit is given and to
carefully set limits for the amount of material to be used, the acreage,
the monitoring and reporting of results. (This same practice should be
used with traditional pesticides as well.)
i. Other Impacts
A probable impact of the proposed regulations is the increase in
the number of permit applications that EPA will receive, and a correspond-
ing number of requests from the applicants to act on the applications as
rapidly as possible. EPA should increase its staff with trained people
to meet this demand. Since many permits are requested in the fall for
experimental use in the spring, it may be possible to shift some of the
EPA staff to meet the seasonal demands of the permit system.
1. Summary of Impacts
The field test portion of pesticide development is very important
to the commercial developer. In addition to obtaining data required for
registration on toxicity, environmental fate, etc., the developer requires
field testing to obtain practical data on application rate, environ-
mental and geographical effects, and most importantly to obtain a market
reaction to the new proposed product. In the past such information was
obtained from federal and state agencies including universities and
colleges (who did not need a permit) and through direct contract with
farmers or through distributors (often with a permit). These resources
may not be as readily available to the developer as previously because
of the restrictions of the proposed regulations (no resale, limited
exemptions, etc.). Thus industry believes that experimental use permits
will, in essence, be a mandatory part of the development process, and as
a result cause increases in costs—more land for tests, increased data
requirements for permit, destruction of crops, etc.—changes in timing—
requirements for environmental data prior to permit, additional delays
in obtaining permit—and increasing risks—lack of marketing data and
performance data compared to competitive products. The proposed experi-
mental use program will reduce any environmental impact of new pesticides
and will provide for better control over the total experimental use of
pesticides.
Most pesticide developers compare the experimental use permit
process and resultant field studies to the "pilot plant" operation of a
chemical industry. It provides an opportunity to determine the practical
aspects of the pesticide, its use and application and to obtain other
information which determines whether the product will be successful or
not—range of cost, acceptance, etc. If this step is essential to the
development of pesticides by commercial organizations, then sufficient
flexibility should be added to the experimental use permit system to
enable industry to obtain these data, given sufficient public health and
environmental safeguards. For example, toxicity data is acknowledged by
all as necessary. Data on environmental fate depends upon the chemical,
its properties, the intended use, locations, area, etc., and may be
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necessary in certain circumstances. By carefully restricting the
quantities which can be used and the acreage, control can be maintained
over the environmental impact. By permitting resale, but still requir-
ing data on use locations, participants, etc., a self-limiting process
will occur on how many locations will be tried by the developer. A
balance between costs of paper work and product purchases and information
to be obtained will be achieved.
Limiting field testing may hide undesirable and unanticipated side
effects until such time as the product is in wide distribution. The
risks in the pesticide development process are sufficiently great that
experimental use permits will probably be obtained by developers under
the new system with as much cost as possible transferred to the ultimate
consumer, including the cost of poor investments pursued by companies
because of lack of data previously obtained under the old experimental
permit system.
4. Restricted Use Pesticides/Certified Applicators
The ie&t>iicted/g eneAa£ a&e cIma-creation 6y6tem and the fieqvuAment&
iofc ceAti^ied appJUxiatofU have Little oh. no dLUiect impact on H.esejwch
and deveiopment activities, in the Aenie that they do wot fieqiuAe additional
data, A-aaeoAc/i activities, expenditure* oi fieseaAjch ^unds, additional
RBV ata£6, on, change the time iname o£ fie&eanxih and development.
One of the major changes in F1FRA, as amended, is the classification
of pesticides for general use, restricted use, or both. Section
3(c)(1)(F) indicates that the applicant for registration must request
that the pesticide be classified for general or restricted use, or both.
Under Section 3(D) the principle of classification system is explained.
If the Administrator determines that the pesticide, when applied in
accordance with the directions for use, or in accordance with widespread
and generally accepted practice, will not generally cause unreasonable
adverse effects on the environment, he will classify the pesticide, or
the particular use of the pesticide, for general use. If he determines
that similar use of a pesticide may generally cause, without additional
regulatory restrictions, unreasonable adverse, effects on the environment,
including injury to the applicator, he shall classify the pesticide,
or a particular use of the pesticide, for restricted use. If a pesticide
is classified for restricted use because of acute dermal or inhalation
toxicity, the pesticide shall be applied only by or under the supervision
of a certified applicator. If the pesticide is classified for restricted
use because it may cause unreasonable adverse effects on the environment,
it shall be applied only by, or under the supervision of, a certified
applicator or may be subject to other restrictions by regulation. Change
in classification may be made by the Administrator; appeals to any change,
as well as original regulations on restricted use, are provided for.
Section 4 provides that the Administrator shall prescribe standards for
certification of applicators of pesticides, provides for both federal
and state certification, and for state plans for certification. Regula-
tions for the classifications of new pesticides shall be promulgated by
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October 1974; all previously registered pesticides shall be reclassified
between October 1974 and October 1976; requirements that a pesticide
be registered for use only by a certified applicator are not effective
until October 1976, and certification of applicators will occur in the
four-year period up to October 1976.
Previous to FEPCA, classification of pesticides and requirements
for certified applicators were non-existent, although many states had
programs for licensing pest control operators.
Although the classification system and use of certified applicators
are separate entities in the law and in the regulations to be promulgated,
they must be combined in considering any possible impact on research
and development activities within the pesticide industry. The classifica-
tion system has not yet been adopted by EPA, and industry has some concern
and uncertainty over how the law will be implemented. As a result,
the possible Impacts of implementation of this part of FEPCA are uncertain.
The following discussion describes industry's anticipation of how the
regulations will evolve, presents some of the problems anticipated, and
summarizes the principal impacts of the restricted use/certified
applicator provisions on R&D activities. Implementation of this part
of the law will have more significant effects on the marketing of
pesticides than direct effects on the R&D process.
a. Anticipation of the Restricted Use/Certified Applicator Program
The law specifically provides for designation of restricted use on
the basis of toxicity or hazard to the applicator or other persons, or
on the basis of unreasonable adverse environmental impact. Industry
generally believes that the restricted use designation on the basis of
toxicity, inhalation or dermal, is reasonable, is justified, and is
important to protect the applicator. Further, industry believes that
toxicity will be the principal determinant of the classification, when
a final classification system is adopted. Industry fears that in some
cases, restricted use will be designated only because of environmental
grounds, e.g., as a result of persistence, although there is acknowledg-
ment that some environmental effects, such as biomagnification, may be
valid cause for restriction. This could lead to differentiation among
products in the registration process with little concern for efficacy,
but placing the importance on environmental effects.
Industry anticipates that a sizable number of compounds will be
classified for restricted use. (Some companies we contacted indicated
that they expect all of their important pesticides for major crop use
would be classified restricted; others, however, felt that they were
working primarily on "safer" pesticides and expected most of them will
be in the general use category.) In either case, there was no great
concern over the number of pesticides classified as restricted, as long
as the criteria for evaluation are consistent. Large companies, with
a broad product line were, in general, less concerned than smaller
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companies. Serious objections were raised by many companies on the
plans to designate a pesticide as restricted use for all its applications,
as opposed to treating each use on a case by case basis. It was strongly
felt that the method of application, type of applicator, acreage covered,
etc., should play a part in the designation of the classification, rather
than the chemistry alone.
Industry anticipates that there will be a large number of certified
applicators after the initial period of standard setting and submission
and approval of state plans. Industry feels that "practically every
major farmer" or "most farmers" will be able to "pay their $2 and be
certified." Industry's general view is that the farmer is becoming more
and more intelligent about the use of pesticides. As long as the tests
for certification are practically oriented and are not based only upon
written theoretical questions, many farmers should be certified. Industry
feels that if there are many restricted use pesticides, there will have
to be sufficient certified applicators or the whole program will be in-
operable. Most likely political pressure in agricultural states will
result in a sizable number of certified applicators.
Industry was uncertain as to whether the designation of restricted
use (with concurrent safety for the applicator and environmental protec-
tion) would allow specific pesticides to be registered more easily than
without the designation, e.g., allowing registration of a particularly
toxic material for a specific important use, because the applicator and
environmental safety was assured. About half felt that this was a
reasonable possibility, the remainder thought it was possible only in
theory or did not feel that this was the intent of the regulations or
would be practical.
b. Problems and Benefits from Implementation
Some of the problems envisioned in the development and implementa-
tion of the law with regard to restricted use and certified applicators
include:
•	Achieving a reasonable balance in the classification system
between environmental and safety criteria for the restricted
use designation.
•	Finding a sufficient number of certified applicators in the
country, if high standards are set for certification.
•	Assuring that the state programs for certification are
adequately organized and implemented, i.e., sufficient
competent state staff, model state regulations, elimination
of cross licensing requirements for dealers and distributors.
•	Providing help to the small farmer, who because of size and
acreage, is unable to obtain services of certified applicator
and may not wish to or be able to be certified himself.
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• Assuring that the "home and garden" oriented formulations
are not affected significantly.
Most of these problems will be solved by reasonable implementation
of regulations by the EPA and cooperation and coordination with the
states.
In addition to the obvious benefits of Implementation of the regula-
tions on applicator (and other persons) safety and protection against
adverse environmental effects, several companies felt that the use of
certified applicator would prevent or at least restrict the tendency of
many pesticide users to "overkill" in the application of products. Others
felt that the increased "Importance" and "availability" of the certified
applicators could lead to good ecological effects, lower overall use of
pesticides and encourage scouting programs and improvements in integrated '
pest management. Others felt that a benefit, or at least a beneficial
Impact, would be the enhanced growth of a "total service concept" in
which an organization provides the farmer with all of the required pesti-
cide services, from seed treatment, through various applications of
insecticides, herbicides, etc., with a guaranteed yield in return for
a portion of the profit. Staff of organizations offering the concept
would be certified and trained in the use of pesticides. Such a concept
may help establish an optimum use of pesticide.
c. Impacts on Research and Development
We found that the general concensus among industry was that there
would be no direct or immediate effects of the restricted use classifica-
tion or certified application program on the principal research and
development activities in the pesticide industry. Secondary effects,
resulting from decreases in potential markets for certain compounds,
or uses, could influence the research decision-making process, and thus
change some of the direction of the research effort.
Industry feels that major purchasers will not greatly prefer the
general use product over the restricted use product because the user
most likely will be a certified applicator, and the more toxic compound
classified as restricted use will most likely be more effective and may
be less costly.
In the R&D process there will always be some uncertainty as to
whether a specific pesticide will be classified as restricted or general
upon registration. If environmental factors become important classifica-
tion criteria, it will be difficult to determine early in the R&D stages
which classification will result because many environmental tests are
not conducted until extended field studies. Thus the research must
continue if the product has promise of effectiveness and competitiveness.
Given two equally effective products for the same market in the early
stages of the research process, one of which would most likely be
ultimately classified for restricted use, and the other for general use,
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industry would normally continue to develop both products until pro-
duction cost and marketing cost information are obtained. If the
general use product had an anticipated equal or only slightly higher
production and sales cost than that anticipated for the restricted use
product, the general use product would be pursued at the expense of the
other. If the restricted use product had a lower production and sales
cost, industry would not shy away from its development because of its
anticipated classification or certified applicator requirements. This
decision may be tempered by the number of certified applicators and
the type of testing required to be certified—if the number is sufficient,
it will not affect the decision to pursue the restricted use product.
In general, industry feels that given sufficient time and money, it
can get almost any good effective product registered. Only if the
restricted use category severely affects the market of the possible
product, and this must be determined on a case by case basis, will
research directions be changed and greater emphasis placed on seeking
the general use product. (There is some belief that the restricted use
categorization could benefit marketing because sales will be limited to
only certified applicators and not to the public, thus reducing the
number of sales contacts and costs incurred.) Some effort in the R&D
process can be anticipated to determine the probable classification of
candidate products, once criteria have been formalized and adopted.
Concerning minor crops and pesticides registered for minor uses,
the general conclusion is that there are so many factors preventing
the development and registration of these products, that the restricted
use category would not severely affect marketing of the product. Industry
is generally unwilling to develop these products, and there may not be
sufficient available products in the future, so that any additional expense or
difficulty of the certified applicator will probably be borne by the user
and passed to the consumer. For uses such as right of way brush control,
where the users are limited but well defined, industry feels the restric-
ted use category will have no effect. There may be some problems in
companies that emphasize home and garden products, if these are classi-
fied as restricted.
Another area of concern, and possible impact, is the reregistration
and classification of existing products. If industry feels that a
restricted use classification could lessen the market share of an exist-
ing product, perhaps because of the existence of a similar general use
product, it may not make the investments required to reregister the
product when the current registration expires. This will most likely
affect minor crops and products used on those crops.
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5. Section 3(c)(1)(D)
Osuglnally A&iongly &u.ppo?uted and now only paAtially Auppo/vted by
JjiduAtny, tkU> taction ofa FIFRA, cu> amended, wtll probably pfwvide
admJjiUtAatbje and ptocexfaAal problem* both EPA and -LndtuMsiy but
Mill have little -impact on tieAexvich and development acttvZtieA.
Section 3(c)(1)(D) of FIFRA, as amended, requires that, "if requested
by the Administrator, a full description of the tests made and results
thereof upon which the claims are based, except that the data submitted
in support of an application shall not, without permission of the
applicant, be considered by the Administrator in support of any other
application for registration unless such other applicant shall first have
offered to pay reasonable compensation for producing test data to be
relied upon and such data is not protected from disclosure by Section
10(b)." The law then establishes the method for determination of payment
and terms or conditions with appeal procedures.
Prior to FEPCA, the Administrator was not constrained from using
data provided by other registration applicants, and no payments for
data use were required, unless it was privately arranged among the
applicants. The data submitted, to our knowledge, was held confidential
with the USDA, FDA, and EPA. However, this procedure permitted the
registration of products by "me too" applicants, those who did not incur
much of the costs of the development process, but could capitalize on
earlier registration of a pesticide by others when the patent provisions
had expired. Industry strongly supported in the inclusion of Section
3(c)(1)(D) in the law "to foster research and development of new pesti-
cides by assuring a degree of protection for the developer in procuring
the efficacy and environmental effects data submitted to the Administrator
to secure registration of a new pesticide."
In November 1973, EPA issued a policy statement clarifying and imple-
menting a portion of this section. The policy indicated that all applica-
tions for registration (new, amendments or renewals) must have an express
offer to pay reasonable compensation for use of test data submitted to
EPA with a registration application for the first time after October 21,
1972. Further, it provided three categories for registration applica-
tion—2(a) where all supporting data was provided in the current
application; 2(b) where references to all data were provided (from open
literature or past applications); 2(c) where registration was sought
under use patterns, efficacy and safety previously established, i.e.,
use of other applicant's previous data although additional new data could
also be provided. The policy also called for publication of the name of
product and active Ingredients in the Federal Register for each applica-
tion, and for the availability of the labeling furnished by the applicant.
A procedure was specified for anyone who desires to claim subsequent
compensation under 3(c)(1)(D) to file notice with the Administrator,
and procedures for proceeding with the applications under 2(a), (b), or
(c) were prescribed. The issue of determination of appropriate and
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reasonable costs for compensation for data was deferred until additional
regulations could be promulgated.
Clearly the intent of the law was to provide some degree of
equitableness to organizations that had borne the costs of a portion of
the research and development activities required by pesticide registra-
tion. In some respects, this section is viewed by industry as an
alternate method of prolonging the proprietary life of a pesticide. One
of industry's concerns was the "me too" registrants, who, under FIFRA,
could produce, market and register a product having ingredients on which
patent rights had expired, with little expense, if any, to achieve
registration. As the registration process became "longer" under FIFRA,
and the available patent protection period shorter, the number of good
marketing years for "me too" companies became greater and the industry
that sustained the R&D efforts could lose part of their market. Thus
3(c)(1)(D) was looked upon as very beneficial to those who conducted R&D
on pesticides.
Our discussions with industry provided a large number of complaints
and opinions on the proposed implementation of 3(c)(1)(D); but, in
general, very few significant impacts on the R&D process could be as-
certained. Some of the principal objections to the proposed implementa-
tion of 3(c)(1)(D) were:
•	Time of Implementation—Only data submitted to EPA in a registra-
tion for the first time after October 21, 1972 is considered for
compensation. Industry feels that the cut off date should be ex-
tended back into FIFRA. Perhaps the reason is that many of the
products in recent "me too" registration applications have
recently had patents expire—the original registration for these
products must have been submitted long ago. Second, many larger
companies feel that there were many "me too" registrations between
October 1972 and November 1973 because a policy was not establish-
ed.
•	Administration Delays and Paperwork—Many companies we contacted
complained about problems in paperwork, i.e., submittal under
2(a), (b), or (c) and having their applications returned with
requests to submit under another category. The 60-day period
before processing under 2(c) also drew criticism. These reactions
are probably due to implementation of a new system and can hardly
be thought of as adding significant delays to the registration
process or impact to R&D.
•	Publication and Availability of Information—There was some con-
cern over publication of information in the Federal Register of
each application; however, all recognize that companies must
some way be made aware of those who would like to use others'
data. There was some concern about the availability of labeling
information. In general, there needs to be a clarification of
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what is considered as proprietary or "trade secrets" under
section 10 of the law, and what information is considered "for
compensation" under 3(c)(1)(D). Industry believes that some
efficacy and application data appearing in the label is a "trade
secret" at the time of registration. Clearly, once a product
is registered and marketed, its label is no longer a trade
secret. A principal objection is that availability of such a
label can give some Information to a potential competitor a year
or more before final registration and could be important in a
competitor's development program. Also, there is considerable
confusion as to the Information that is publicly available under
the Freedom of Information Act as compared to Section 3(c)(1)(D)
under FEPCA. It may be that 3(c)(1)(D) is under criticism for
unjust reasons.
•	Interference with Intercompany Arrangements—Some organizations
believe that 3(c)(1)(D) is unnecessary because it Interfers with
licensing and agreements to manufacture, distribute, etc., which
exist among companies. In any case, there is probably little
affect on any R&D activities of these companies since they can
now and should be able to continue to agree on reasonable compen-
sation with or without the EPA procedure.
•	Establishing Appropriate Compensation—Although detailed procedures
for establishing appropriate compensation have not been proposed,
many feel that the compensation issue will have to be resolved
in court soon. The general conaensus of the larger companies
is that the compensation will be too low; yet several do not
want a case brought to court now to set precedents for the
future. All agree that if a reasonable compensation is provided
for, the industry and the public will benefit from 3(c)(1)(D).
Of course, one's definition of reasonable depends upon whether
one is the buyer or the seller.
•	Other Impacts—Several industrial representatives felt that an
effect of 3(c)(1)(D) was to prevent publication in the open
literature of recent data on pesticides. They felt that this
would impede hiring of good research staff who felt the need to
publish. Although we agree that, prior to registration, there
is little incentive to publish, afterward there is every reason
and we believe this issue has little impact on R&D
effort.
In the long term, implementation of 3(c)(1)(D) will be marginally
beneficial to industry's R&D efforts. After the initial administrative
procedures have been fully developed, some reasonable values have been
set for the data to be used in registration, and clarification of trade
secrets and compensatable data is made, the intent of the law will be
achieved. The impact on R&D activities will, in general, be small.
Unless the value set on the compensatable data is higher than industry
now estimates, the amount will be small compared to the total development
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cost of the pesticide. Companies are probably not going to conduct
additional R&D in the hope that they will be compensated when someone
else uses the data for registration of a product.
Sufficient process work, product development, and marketing efforts
will generally have been undertaken so that the "me too" registrant
cannot easily catch up without some expenditure. The cost of the
compensatable registration data will probably be small compared to the
"me too" company's production and marketing costs if the company is to obtain
significant market penetration. Elimination of the "me too" companies
by setting too high a value on data is not in the best interest of the
public. The general consensus is that economic conditions and the free
enterprise system will eventually have much more impact on R&D efforts
(and pesticide production practices) than the 3(c)(1)(D) implementation.
6. Reregistration of Existing Pesticides
The mnegi&tnation o£ cwuvently ne.gi&tene.d pe&ticide.* in ac.c.onda.nce.
with the, new pnovisionk FEPCA most likely wiJLl incAe.a&e non-innovative
ne.Aeato.h and de.ve.lopme.nt activities by indu&tny ^on a two- to faive-yean
peniod and wiZl catalyze, the nemovaJt otf pnesent manginally pnojitable
peitixude.6, paAticulakly thobe Ion. minon caop cue, finom the. manket.
Indu&tny hoi given tittle attention to nenegiit/iation to date because
oi othen. mone. pneAAing i66u.es associated with FEPCA implementation.
FEPCA, under Section 6, calls for cancellation of the registration
of a pesticide after a five-year period from original registration,
unless a request is received from the registrant, or other person with
the concurrence of the registrant, for continuation of the registration.
Publication of intent to cancel will be made in the Federal Register.
This is essentially the same provision as that given in Title 7, Ch. Ill,
362.10 (i) of the Regulations for the Enforcement of FIFRA, with the
exception of the publication of intent to cancel.
A more important part of FEPCA, with respect to reregistration,
may be the section describing the effective dates of the provisions
of Section 4, Registration. The law indicates that "after two years,
but within four years after enactment of this Act, the Administrator
shall register and reclassify pesticides registered under the provisions
of FIFRA prior to the effective date of regulations promulgated under
Section (c)(1) [October 1974]."
There is some concern as to whether the above requirement means
that all previously registered pesticides will require reregistration
(with appropriate pesticide classification) within that 2-year period,
or whether only the classification of restricted use or general use will
be made. The general belief is that only reclassification will occur
and that reregistration will be required only at the end of the normal
5-year period. However, additional data may be requested by the EPA
to support the reclassification procedure. Much of industry is adopting
a "wait and see" attitude toward registration, or are doing very little
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towards this goal, except as their current registrations expire, because
they are uncertain of the procedures to be followed.
We believe that each currently registered pesticide will be carefully
examined by its registrant when reregistration is required (after the
guidelines for registration and restricted use classifications are
issued). If the product is (1) marginally profitable, (2) has a relatively
small volume, (3) is expected to be classified for restricted use, (4)
will require considerable new data on toxicology, environmental degrada-
tion, or environmental effects, or (5) has little or no patent coverage,
the tendency will be for its developer not to request reregistration.
We were given examples of specific products by several companies that would
not be reregistered, because the cost of obtaining the added data would
be greater than the reasonable projected income over the next few years.
Most companies feel that the greatest additional data requirements will
be in environmental effects. For most of these compounds, there were
only small markets, mainly on minor crops. Some narrow spectrum pesticides
will also not be reregistered; this would be counter to the emphasis of
EPA.
The number of pesticides that will not be reregistered will depend
primarily upon how much additional data is required and the market size.
A product which was originally registered in 1970, after PR 70-15, may
need only modest additional data, and thus if a reasonable market exists,
the necessary reregistration effort will be expended. Estimates of the
additional effort required for reregistration range from 0.5 to 6 man
years per product. One problem expressed by several groups was the ex-
tension of time for reregistration; for example, if additional 2-year
carcinogenesis studies and other long-term studies were required.
This reregistration effort will to some degree detract from innova-
tive research and development activities; it will require more analytical
chemistry, field testing and additional regulatory support efforts. With
a limited number of staff, effort will be withdrawn from the search for
new products or innovative activities, which may have more risk than the
reregistration of an existing marketable compound. Each compound will
require its own cost/benefit analysis for specific products in making
these decisions. Simply stated by one organization, "if the product is
hot, it must be reregistered; if not, we will forget it."
It must also be remembered that there is a natural attrition of
pesticides as they outlive their marketability and as they are replaced
by other more effective, less costly, or more profitable products. This
causes industry not to reregister certain products as a general business
decision. Since data requirements under the new law have not changed
drastically, we cannot expect drastic changes in current practices of
industry in dropping products when they are no longer useful and
profitable. However, the emphasis on environmental effects in FEPCA and
the registration uncertainty will probably increase the number of product
dropouts. This will have the beneficial effects of an overall reduction
in potential adverse environmental effects, and in the long-term provide
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more incentive for industry to give greater emphasis for the environment
in its pesticide development process, but at the expense of neglecting
means to protect small volume crops.
7. Other Specific Impacts of FIFRA, as Amended
Table 9 In Section IV B indicated a number of other changes as a
result of passage of FEPCA and the regulations promulgated or proposed
to date. From our discussions with industry, we believe that most of
these changes will have only minor impacts on the research and develop-
ment activities in the pesticide industry at the present. There may be
specific problems for industry created by these portions of the law and
the regulations, which could result in an increase in cost or increase
in effort in pesticide production. However, there will be little, if
any, Impact on R&D activities. Some of the principal comments of industry
and any related impacts of these portions of the law are briefly discussed
below.
a.	Indemnification
Section 15 provides for indemnity payments to persons who owned a
pesticide, the registration of which was suspended or cancelled because
of actions necessary to prevent imminent hazards, and who suffered losses
by reason of the suspension or cancellation. At the beginning of our
study we hypothesized several possible effects could occur: (1) EPA
could be more cautious in granting registration because of the possi-
bility of indemnification and required payments; (2) once registration
had been granted, EPA would be cautious about suspension or cancellation
to avoid indemnification; (3) industry would feel that this clause
reduces some of the risk in pesticide development and as a result would
be willing to try more innovative approaches with certain potential
pesticides. From our discussions with industry, and limited discussions
with EPA staff, we conclude that none of these original hypotheses are
valid. Industry, in general, feels the indemnification section will have
no effects at all on the pesticide R&D process. The general consensus
is that new chemicals are always given a cautious and extensive review,
indemnification will not make the review more cautious or thorough.
Second, industry believes that if any valid safety or environmental
reasons are found to suspend or cancel a registered pesticide, EPA will
exercise its authority (and obligation) without consideration of indemnity.
Third, industry doubts it will ever recoup significant losses through the
indemnity clause. The risk in pesticide development is not reduced, and
with the current review process, Industry doubts if any new registered
pesticides will be recalled or suspended quickly. Several industrial
contacts considered that this section "opened a can of worms," but did
not believe there were strong impacts on R&D.
b.	Books and Records/Registration of Establishments
In general the provisions of the books and records sections of FEPCA
are very similar to those of FIFRA. Industry expects greater inspection
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and enforcement of these books and records, and as a result may Incur
some extra effort and expenditure in assuring their completeness and
availability. However, the information required is generally available
from company records and the impact of the law is felt by industry to be
only another "administrative headache." The books and records section
may add some work to formulators and those who prepare chemicals on a
contract basis. No effect on research and development is anticipated.
Registration of pesticide establishments also will provide little
impact on research and development activities. Administrative effort
and expense will be required to assure that labeling is correct, to
account for the large number of manufacturing facilities any one company '
may have, etc.
c.	Packaging and Disposal
FEPCA provides that the Administrator shall establish procedures
and regulations for disposal and storage of packages and containers of
pesticides and excess amounts of pesticides. Industry, in general, is
concerned about the problem of disposal of packages and containers,
and pesticides themselves. The impact of the regulation is unknown.
Various segments of industry have been working on the problem. Some
large companies conduct their own packaging research, some of which is
on "disposable" or "degradable" packages. Others support the efforts
of NACA in this area. The research and development activity in packag-
ing and disposal is at the moment modest. There is some concern for
"child proofing," the development of disposal sites for pesticides,
economic approaches to recovery of pesticide containers, etc., and the
general feeling that "some day there will be a significant container
disposal problem." Industry feels that this "low level" of research
and development activity will continue but that FEPCA will have little
overall impact. In general, they are more concerned with disposal
problems under the effluent guidelines regulations and ultimately under
the provisions of the Hazardous Waste Management Act,
d.	Unlawful Acts, Enforcement, and Penalties
As mentioned earlier, the series of unlawful acts, methods of
enforcement, and penalties involved in FEPCA are all "stronger" than in
FIFRA. These provisions, by themselves, do not change the research and
development activities of the industry. Industry expects greater en-
forcement, receipt of severe penalties for violations, ^nd careful
scrutiny by EPA (both the OPP and through regional offices). They expect
as a result that they will have to be cautious and careful in all of
their operations, particularly those involving administrative actions,
records, shipment, inspections, permits and labeling. They believe that
they are very careful and cautious now in actions dealing with safety,
environmental effects, data reporting, etc., since it has always been in
their best interests, and as a result no significant impacts of the new
law will result. Some of the larger companies felt that the increased
costs of the entire pesticide operations as a result of any additional
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caution, records keeping, etc., to avoid penalties, would also discourage
the continued efforts in pesticide for minor crop applications. Further,
they felt that whereas the major producers could afford the occasional
mistake, leading to a penalty, the smaller companies could not. This
Tould make the operation of small companies more risky, and ultimately
reduce the number of marginal or minor companies in the field.
e.	Intrastate Coverage
FEPCA also regulates pesticides produced and used, entirely within
a single state. The nature of the Industry—a limited number of establish-
ments conducting research and development, most of which sell and ship
pesticides to several states (and internationally)—is such that little
impact, if any, on R&D activities will result from the addition of intra-
state coverage. There may be some significant changes in the total
activities of formulators and distributors because of FEPCA but these
elements do not contribute significantly to the R&D output of the pesticide
Industry.
f.	States Authority
Under FEFCA state authority has both been partially extended and
restricted. States can regulate the sale or use of pesticides, but not
in contradiction with sale or use prohibited by EPA; states cannot require
additional labeling or packaging requirements; states can provide registra-
tion for pesticides to meet local needs if the state is certified by the
Administrator, and if registration for such a pesticide has not been
denied, cancelled or disapproved by the Administrator.
The impact of these state authorities on research and development is
probably small. However, there is some general concern that some states
may not be able to handle the requirements for registration to meet local
needs. Most likely these states will not be certified by the Administrator
to register "local use" pesticides. Thus the agriculture and other
industries In these states may be deprived of some pesticides. Industry
would like help from EPA in providing guidance and support to these
states. Another concern is for more coordination generally between the
states and EPA to assure that the standards for applicators to be
certified and experimental permits to be issued by states, are uniformly
Imposed by the states. Generally, Industry expects a number of state
problems In disposal, certified applicators, etc., but feels that little
Impact on R&D will occur.
D. GENERAL IMPACTS OF LEGISLATIVE AND REGULATORY ACTIONS—RELATIONSHIP
WITH OTHER TRENDS
In the previous section we have described the specific impacts of
the various sections of FEPCA on research and development activities in
the pesticide industry. These impacts are interactive, and some broad
changes and trends in the pesticide R&D process can be anticipated as a
result of their combination. Furthermore, there are general trends in
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the Industry related to economic considerations, the energy crisis,
shortage of raw materials, increasing labor costs, political and public
pressure to increase agricultural production, etc., which also produce
trends and changes in the research and development process for pesticides,
particularly when combined with the impact of legislative actions. In
this section, we will present some of the general impacts and changes
anticipated in the industry, including a discussion of how the trends
described in Section 111 relate to R&D. Then we will briefly describe
some of the more important benefits to the public and to industry of
the implementation of the current law.
1. Research and Development Costs and the Direction of
Research Effort
As illustrated in Section III, the costs of the various portions of
the research and development process has been increasing as a result of
additional data requirements, extension of the time frame, and other
regulatory activities. In general, synthesis costs have not increased
significantly beyond the normal inflationary increases for all R&D
activities. The cost of primary and secondary screening of pesticides,
activities conducted generally in the laboratory, has also not increased
greatly. Significant increases have occurred in the field test portion
of pesticide research and development, in the laboratory and field work
required for development of safety and environmental data (residue,
toxicity, metabolism, environmental fate, etc.), and in the administrative
efforts required to achieve registration. Of course, all costs have
increased due to inflation over the last few years. The question to be
discussed here is: what is the feedback or resultant effect on the
pesticide R&D process as a result of increasing costs of the various
segments of the process?
Considering first the overall economics of a pesticide industry,
the percent of product sales devoted to research and development is
relatively constant or at best has been increasing slowly. The percentage
of sales devoted to R&D depends greatly on the individual company. In
general, the quantity is several times higher than traditional of the
basic chemical industries, but not as much as that spent by the
pharmaceutical industry. Values of 4 to 8 percent of sales are typical.
Sales of pesticides have also been increasing over the last years, although
there has been a considerable decline in sales of older, harder pesticides,
such as the chlorinated hydrocarbons. The greatest increase in pesticide
sales has come in the area of herbicides, particularly new herbicides
for use with major crops. Thus, the total number of dollars available
for research has been increasing roughly in proportion to sales.
The net effect of these factors, combined with current economic
trends in the agricultural chemical industry, is a change in the balance
of research effort to increase efforts which bring short-term return on
the R&D investment, and to reduce the effort which can bring long-term,
but relatively uncertain, return. Specifically, there is a greater
emphasis in most companies to capitalize on existing products. Research
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emphasis is placed upon conducting the required "defensive research"
to maintain the registration of products for existing uses. Maintain-
ing the registration of a proprietary, patented product which is sold
competitively in the marketplace, takes priority because it is the least
risk road to profitability. Research emphasis is also placed on those
studies required to add new crop uses to existing products, provided
there is sufficient market. As a corollary to this emphasis, there has
been a general decrease in funds available for long-term research and
.development investments, thus this longer range R&D must be more selective.
Several companies have dropped research in areas of marginal sales or
profitability, i.e., fungicides, nematocides, certain insecticides, etc.,
and minor uses. Second, emphasis on new, innovative approaches to
pesticides has been reduced since this investment has even more risk
than investment on conventional pesticides. Finally, long-term research
investments have concentrated on the major agricultural markets at the
expense of minor crops, right of way, home and garden supplies, etc.
This change in balance between short-term research for short-term return
and research for a longer term return varies with a specific company.
Smaller companies which are more dependent on the profit from the sale
of a limited number of compounds must emphasize the short-term return and
thereby devote most of their work to maintaining and adding product uses
to their currently marketable products. This may be somewhat short-
sighted since it does not place them in a good competitive position for
continuing in the marketplace 10 years in the future. The larger pesti-
cides companies, on the other hand, and particularly those with sufficient
capital resources, either as a result of major agricultural products or
parent companies with a large base of industrial operations, can afford
to continue their relatively high level of commitment to longer term
research efforts.
In parallel with shift in emphasis, another trend, supported by the
data given in Section III, is that the number of compounds which are
developed and reached the marketplace is decreasing. As a result a
greater number of compounds are permanently placed on the shelf at some-
time during the screening and evaluation process. The screening and
decision-making process must become more effective in that approximately
the same number of compounds or perhaps even an increased number are
entering the screening process. Factors that can ultimately effect the
decision to go ahead with a particular product are, however, being used
in the screening process at earlier decision points. For example, more
effort may be placed on developing better estimates of production costs
of pesticides, in order to make a determination of possible product
competitiveness early in the process. As environmental concerns increase
and if the trends in pesticide registration show that "environmentally
safe" pesticides ultimately will be registered more easily than others,
effort in environmental research will be needed to provide an early
input to the decision-making process. There will also probably be a
change in the synthesis approach to be more selective—use the "rifle
shot" approach to pick chemicals for initial screening rather than the
"shotgun" approach.
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The end result is an increase in the number of possible pesticides which
are "on the shelf." These are primarily chemicals with low efficacy, high
production costs—chemicals which would never become commercialized because
of economic or other reasons. The classification provisions and certified
applicator system implemented by current law and regulations could help
get some of these compounds off the shelf and into the market for special
needs because more toxic compounds may be registered. Nevertheless, it
will be increasingly difficult to find compounds that are comparatively
better than those already on the market.
Another way of expressing some of the changes resulting from the
increased cost of the pesticide R&D process is that the threshold for
developing a winning pesticide has changed. The R&D dollar expenditures to
develop this winner have increased, both for the specific product and for the
product considering a number of other potential products which have been
discarded. The market threshold for deciding to go ahead with any particular
Product, must necessarily also increase since the percent of sales devoted to
research and development has been maintained about constant.
From a management viewpoint, there is little incentive to devote research
and development dollars to innovative pesticide efforts with a high risk
of long-term development, i.e., little or no return for at least seven to
10 years (the time for registration and initial marketing) when a short-term
gain can be obtained by extending the use of a particular, already developed
product to other crops.
Another impact of the increased cost of the R&D effort is for companies
to seek an international market early to bear some of the costs of registra-
tion in the United States. A portion of the research effort is also being
done internationally by the larger pesticide companies with only the necessary
field tests and evaluation done iu the U.S. The importance of the international
market is increasing in the decision-making process.
The following changes in research direction occur:
•	There is generally no change in the number of compounds synthesized
and placed through the primary screen.
•	Emphasis in the synthesis and screening process is placed on
analogs and homologs of existing or already registered products
rather than diversification into new or innovative types of
pesticides.
•	To some extent less effective compounds are pursued i£ they show
great promise of safety and environmental acceptance and can
replace existing more hazardous products.
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•	Efforts to simplify and streamline the screening process in terms
of new instrumentation and better techniques are continuing.
•	Emphasis is placed on development of analytical techniques and
refined, but cost effective, methods of conducting environmental
tests, residue analysis, metabolism studies, degradation studies.
•	Research which is not in the "main stream" of pesticide development
is done more and more under contract to research organizations, e.g.,
toxicology, carcinogenesis, toxicity to fish and wildlife, etc.
•	There is a reduced emphasis on long-term programs in areas outside
the traditional chemical pest control.
•	Management demands more extensive and accurate data to support
the cost benefit analysis in the decision to go ahead with a
compound. This involves a more thorough examination of toxicology,
environmental effects, as well as the process development itself.
2. Timing of the Research Process
There are three principal impacts of regulatory actions on the timing of
the research and development process in the research and development industry:
(1) an overall extension of the R&D process, with most significant impact on
field studies and on data development for registration; (2) a re-ordering of
parts of the research and development process with some changes in importance
of the elements to the decision-making process, (3) iteration of portions of
the R&D process brought about by EPA data requests and the need for better
decision-making. Evidence for the overall increase and timing of R&D process
and some of the reasons for the increases have been given in Chapter III.
Over the past 15 years there has been a relatively continuous increase in
the time period from synthesis or initial screening through registration
of from 4 to 7 years over the period from 1960 to present. As mentioned
earlier, some of the reasons for these increases in the overall time span
have been the requirements for additional data—toxicological, environmental
impact, residue, metabolism, runoff studies, carcinogenicity, teratogenicity,
etc.—the delays in processing of information within the EPA and delays in
reviewing requests for experimental permits and registrations. Other factors
include the increased importance on obtaining reliable data for the decision-
making process, the difficulty and need to obtain reliable market data for
decision-making. In terms of re-ordering portions of the R&D process,
toxicological work has now been moved up so that more extensive work is conducted
earlier in the R&D process. Similarly the requirements for part of the two-
year tests for carcinogenicity, etc., being necessary for the experimental
permit, make it important that these tests be started fairly early in the
process. Industry anticipates that a similar moving up of environmental
studies may eventually occur so that some more environmental work is done
prior to extended field studies, than presently practiced. Similarly, there
is a greater amount of earlier effort in analysis of the potential production
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processes and preliminary engineering design to access the costs of potential
products. Some companies that have been willing to expend a heavier rate of
resources early in the process have actually been able to decrease the
process duration. However, most companies cannot exert this additional
effort and their resources get divided among the efforts which are necessary
at this early stage.
Most of the re-ordering of the research efforts is done in an attempt
to make the decision-making process more effective and more accurate. If
more effort is required earlier in the R&D cycle where a greater number of
compounds have not yet been eliminated from the development pipeline, the
overall costs of research increase as explained earlier. Thus there is
conscientious effort to reduce the number of compounds at any stage in the
process through focus on important decision points and more continuous
review to eliminate products at the earliest possible stage. Thus the re-
ordering of the R&D process can lead to increased efficiency in the R&D
process.
The re-ordering of the R&D process also impacts the decision to invest
in new production facilities. In the past such decisions were often made
so that the granting of registration would correspond closely with the
completion of plant construction and product availability for the market.
This was true for both pilot facilities to produce pesticides for experimental
use as well as for full-scale production facilities for general sale.
Because of delays in registration encountered by several in industry and
because of the desire of management not to commit large amounts of money
for construction until the risks have been reduced as much as possible, the
decisions for plant construction are now made closer to the end of the
registration process than previously. The increases in the time required
for plant construction and startup (not due to regulatory actions in
general) further extends the time from which the product was first developed
to when production in reasonable quantities can be achieved. The timing
of the decision for plant construction process depends on the individual
company, whether there are alternative facilities for manufacturing the
pesticides, whether the intermediates are purchased from other companies*
whether the raw materials must be purchased or are available within the
company, and many other factors. Additional delays in getting production
facilities on stream near the time of registration cannot be attributed to
changes in pesticides regulations; in fact, the major influences on these
delays are general economic constraints.
Lengthening the overall R&D process and re-ordering of priorities and
procedures within the R&D activities have caused a secondary problem in
terms of decision-making. The R&D process for most pesticidal chemicals
has become close to the "half life" of a manager of the R&D process opera-
tions. As a result it becomes more difficult for a manager to see the
product through from beginning (synthesis) to end (registration). This
results in lack of association of specific people with specific products
and less motivation or inspiration for continued development effort. The
extended duration makes the development process "a little less exciting,"
and leads to a decrease in motivation of all the participants.
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Another impact of timing relates to iteration in the R&D process as
it now is conducted. Requests for additional data from the EPA, changes in
data requirements and guidelines, or changes in regulations may occur during
the development process of a product (for example the PR 70-15 change, a
change from FIFRA to FEPCA, all of which would occur during the development
process of a pesticide first synthesized in the period from about 1967 through
1970). As a result, work in several different segments of the R&D process is
never completed but left open-ended for continued effort at a later date.
Toxicology studies may be performed over several years time, with concentra-
tion of efforts at various points, whereas in the past it may have been done
at one time by a group of individuals working on a particular chemical. To
some extent this reiteration process can lead to inefficiency, lack of
motivation or incentive, and lack of productivity.
3. Staffing of R&D Activities
Although the impacts of legislative and regulatory changes on the
R&D staff of a specific pesticide company depend greatly on its size and
type, some general conclusions can be drawn. The R&D staff of the pesticide
companies who conduct innovative research and development has increased.
The number of biologists, environmental chemists and engineers in particular
have increased. Also the number of people involved in regulatory liaison,
and in patent and legal departments, have increased. The field test staff
has remained about the same, although significant changes are anticipated
as a result of the proposed experimental permit regulations. Some interchange
or substitution of staff from one job to another has occurred. It has
generally not been possible to use the synthesis chemist in work requiring
environmental biology, entomology, or in regulatory liaison. However,
chemists with a strong analytical background can participate in environmental
chemistry, residue studies, etc., areas which have seen a large increase
in labor requirements to meet the data requirements of registration.
There is a reasonable amount of mobility among the staff in pesticide
companies. In our discussions with industry, we found that frequently a
manager or researcher with one company gained experience at another company.
People who leave major companies because of a cutback of a particular phase
or area of the research program often find similar jobs in the same specialty
in other companies. Companies vary somewhat in their staffing policy;
smaller companies and some larger promote the "family" feeling—provide long-
term security for its employees and promote from within as in many other
chemical industries. R&D staffing in the pesticide industry is probably
not significantly different than in most chemical or pharmaceutical companies.
Another effect of the regulatory process on R&D staffing is for
companies to focus in certain market (and R&D) areas, i.e., herbicides,
insecticides, etc., and to build centers of expertise in these areas.
Specialization has also occurred through the more extensive use of outside
contractor support in the pesticide R&D process. Several companies
subcontract their toxicology efforts, some environmental biology, analytical
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chemistry, or fish and wildlife studies, to other laboratories. A few
companies have gone even further by having their screening done on a contract
basis; others are beginning to have their field test work done by contractors.
Frequently this specialization results from a desire to reduce the costs of
the pesticide R&D process and to focus on those portions which are more
critical to the pesticide development process, rather than those which fit
only into specific registration requirements.
There is considerable diversity of opinion among industry as to where
new R&D staff should be added. Many larger companies would prefer to see
new staff added to promote innovative research and the development of new
products, primarily new chemicals. Other companies would prefer to see staff
added to development efforts associated with additional registration^ of
existing compounds on other crops. The greatest increases in staffing in
most companies have occurred in "defensive research" and in "field develop-
ment studies" so that registrations can be maintained and new products added
to the registration.
In summary, we expect a slow but relatively steady growth in R&D staff
within the industry, partially due to legislative changes, with concentration
on analytical chemistry and environmental science.
4. Patents
As part of this study, we attempted to assess the significance of
patents and patent protection to the R&D activities in the pesticide industry.
Very mixed reactions were obtained in our discussions with industry on the
importance of patents. Most companies concluded that as a result of the
extension of time required for pesticide registration, the remaining useful
patent life of most pesticides is about 10 years. Practically all companies
would like to extend this patent life through issuance of the patent at
the time of registration or through a patent system such as that used in
England where extension of the patent life is granted if a company is unable
to exploit a patented product because of unforeseen events, natural
occurrences, government regulations, etc. Industry realizes, however, that
it may be almost impossible to change the patent process for pesticides
over the near-term, particularly without changing the process for all other
proprietary type of products as well.
Industry generally files applications for patents as quickly as possible
after some pesticidal activity for a chemical has been demonstrated. Most
companies believe that most of the original investment can be returned in
the 10 years of useful patent life obtained, assuming a 7-year development
time for the pesticide product. Even after the patent has expired, the
fact that the development effort, testing, and production facilities have
probably been written off, the experience and know-how gained in producing
the product, as well as the marketing position achieved, makes it difficult
for other companies to competitively price the same product and obtain a
significant market share quickly. Although many companies stress the
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Importance of patents and have large patent staffs, they are more concerned
about their ability to get particular products registrered than they are
to assure an extra amount of patent life for their products.
The trend in some companies recently has been to try to obtain a patent
at an "optimum time," i.e., at a time early enough to protect the product
yet keep as long a patent life as possible. We expect this trend to continue
particularly in view for the requirements for publication of product names
and formulas in the Federal Register during the experimental permit process
and the availability of data under the 3(c)(1)(D) provision. All of the
companies which we contacted indicated that they had not been significantly
hurt by patent problems in the past and did not expect to be in the near
future.
Originally we had believed that a number of patents issued during a
certain time period would be a good indication of innovative activity in
the pesticide industry. A review of number of patents issued over a 15-
year period indicated no consistent trends. There were several consecutive
years in which large numbers of patents were issued and many years in which
a relatively modest and constant number were issued. From our discussions
with industry and patent attorneys we conclude that some of the variations
observed were indicative of patent policies, changes in the Patent Office,
the manner in which classes of patents are issued, etc., and not a measure
of the innovative activity. Furthermore, it was a general consensus of
industry that many patents are filed as defensive measures, that is, paper
patents to prevent other companies from patenting the same or similar
compounds even though the effectiveness or usefulness of the product has not
yet been determined. Patent protection at this early research stage is another
measure of insurance for the major pesticide companies. We obtained several
examples from industry which indicated that in a particular year's period
only a few products were registered, but a large number of patent applica-
tions were filed. This trend continues and suggests the protective nature
of many patent applications. A portion of industry feels that present
patents are becoming more and more narrow in their coverage. As a result
companies are having to rely more on developing a strong production and
marketing position rather than relying as much as in the past on patent
protection.
One area in which additional patent protection is needed is biological
controls. A common concern of those few industries pursuing this area of
pesticide research is that they cannot obtain patent protection for a
proprietary product. Several people believe that patents will eventually
be useful in biological control applications, primarily for techniques of
formulation, methods of preservation, or means of distribution, instead
of patents on the basic pesticide material, bacteria, virus, etc., which
are not possible. Process patents will also be obtained but most people
do not feel that these will be too valuable.
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In summary, industry has more concern that the market share and
profitability of a particular product will decrease because of the entrance
of new competitive products than concern over the loss of a year in the
available patent life as a result of extension of the R&D process.
5* Pesticides for Minor Crop UseB
Of particular concern to the EPA, the public, agriculture and to industry
is the possible reduction of the number of pesticides registered for use on
minor crops. This reduction has been brought about by legislative action
to some extent, because of the increased costs of obtaining registration
for a product whether it is registered for a minor or major use. The
data requirements for pesticide registration for major and minor uses are
similar, i.e., toxicological data, residue data, field testing, carcinogenicity*
etc. As a result the costs of the R&D process for minor crop products may
not be significantly different from those for major crop products. There
will be a difference in development effort required because of the more
competitive nature of the market for pesticides for major crops. However,
because of the much smaller market for the pesticide for minor crops, the
return on investment is significantly less. The minimum "market size" for
a product ranges from about $500,000 for a small pesticide company to a
$100 million market, with a 10% profit, for larger companies. Industry
pursues those chemicals more vigorously which have potential application
to major crops such as corn, soybeans, wheat, small grains, etc. The
decision is made primarily on the basis of economics. If there is a
sufficient market for a product to return the R&D investment and make a
reasonable profit for a specific company, there is considerable incentive
to develop that product. Both profitability and volume must be combined
in making this decision. Once a product is registered for a major crop,
there are incentives to extend its registration to minor crops: (1) for
public relations and to place the company into a preferred position for
selling its products to the major market, (2) because most of the work in
environmental fate and toxicity may already have been accomplished and thus
only limited residue and other studies need to be done for the minor
crop, (3) it is beneficial and economical to capitalize on available plant
production, marketing efforts and distribution channels for a product already
developed.
Several companies adopt the philosophy that if it will be "easy" to
obtain the registration for a particular pesticide, the company will pursue
the product even though it may be a minor crop use. Most larger companies
believe that three to five uses, i.e., three to five minor crops, would
be necessary to support the development of a pesticide used only on
minor crops. Other companies believe that their "exposure" is greater with
pesticides for minor crop use, i.e., they can be easily sued for product
performance, their cost for development are almost as large for major
crops, and the risk is higher.
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A general conclusion is that changes in regulatory action as well as
general economic conditions will lead to a decrease of number and
availability of pesticides specific to minor crops. Pesticide development
for major crops will be extended to minor crop uses where possible. The
decisions will be made on a case by case basis by balancing the necessary
added investment with the return provided by both the volume of the market
and the profitability of the pesticide. One can expect to find chemicals
on the shelf which are suitable for minor crops but which will not be
developed because of these economic considerations.
Some of the recommendations made by industry to assist in assuring
availability of pesticides for minor crops include: states and state
laboratories assist in the development of pesticides for minor crop uses,
the EPA provides more active support for the development of pesticides
for minor crop, uses, the IR 4 program be expanded and improved to aid the
farmer in increasing the availability of compounds for small crop uses,
and that some of the registration requirements, i.e., data requirements
for minor crop uses, be dropped so that the cost of registration is
decreased.
6. Differences in Impacts Among Small and Large Companies
In previous sections, we have indicated where specific regulations may
have different impacts on companies depending upon their size and available
resources. Here we will briefly summarize some of these differences and
point out specific problems of the smaller companies involved in pesticide
research and development.
In general, the impacts of the regulations and their implementation can
be better absorbed by the large diversified companies that do pesticide
research (divisions of major oil companies or major chemical companies)
than by the smaller companies. The factors which lead to this result
include:
•	The usually greater long-term commitment to pesticide development
of the large companies.
•	The availability of capital for both R&D and production facilities
of the large companies.
•	The availability of external resources through other divisions
or subsidiaries of the large companies.
•	The multi-national approach to R&D and marketing of the larger
companies.
•	The normally larger mix of products and organization of the
marketing activities of the larger companies.
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The long-term commitment allows the larger companies to cantinue a
reasonable level of basic R&D and new synthesis and screening work somewhat
independent of the needs for expanding and maintaining the current product
lines. The availability of capital permits more timely decision-making and
plant investments, as well as the ability to take higher risks in developing
pesticides that may or may not be winners. The availability of resources
from other parts of a large company make it easier to deal with problems
of effluent guidelines, plant design and construction, extra loads in
analytical or pilot plant facilities, packaging and disposal without
resorting to contract assistance or extra staff to meet these demands.
The availability of resources in other countries for testing, screening,
synthesis as well as ready availability of markets to yield initial return
on investment, provided by multi-national companies adds to the stability,
of the large company and its ability to absorb specific regulatory impacts.
Finally the larger mix of products allows more effective use of distributors,
experimental farms, marketing information for decision-making, etc., and
provides more opportunity to extend the product line by adding new uses to
existing products.
The smaller companies that conduct R&D in pesticides have several
advantages, which probably do not counter balance the factors mentioned
above. It appears that the R&D efforts of the smaller company are more
directed or focused and are more innovative. Smaller companies operate
with a lower overhead, are willing to accept smaller markets for their
products, and are willing to specialize more to some extent (for minor
crop use, or for biological controls, as examples). Unfortunately, it is
the belief of most people in pesticide research that EPA legislation
discriminated against innovative activity. However, recently proposed
regulations have stressed the importance of these biological controls.
The provisions of the regulations that encourage integrated pest management
and biological control approaches are being challenged by the larger, more
established companies.
Many of the larger companies feel that the passage of FEPCA is more
of an annoyance, another regulatory process that must be dealt with, than
a threat to research. They have the long-term commitment and resources to
deal with the regulatory problems. The smaller companies cannot afford the
added expense and still maintain profitability.
As a result of these' differences in impacts, we expect that the major
pesticide developers will continue their R&D activities at the present level
almost independent of the regulations, although internal shifts in staff,
timing, and product emphasis will occur. These companies will pursue the
major market areas and major crops and will probably not venture far into
innovative pest control approaches. Increased pesticide use, and the slow
but steady development of new pesticides will allow these companies to
grow to meet new market demands.
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Some of the smaller companies will slowly be diverted from a vigorous
research posture. Introduction of competitive products, or the forced
withdrawal of a product from the market, can Impact the small company
seriously unless It has sustained an Innovative R&D program on new pesticide
development. However, the cost of innovative programs 1s sufficiently large
and requires a continuous long-term effort so that research in many small
companies will probably give way to the need to maintain the existing
product line and register new crop uses. Thus, in time, some of the small
companies may be forced out of the business of innovative research and may
become only producers and formulators. Those small companies that have
learned to specialize in particular product areas, and that have directed
their R&D efforts to well known and established markets, will probably be
able to maintain a sufficient flow of new proprietary products to achieve
financial success. We expect that these companies will be essential to
providing innovative approaches to pest control, and recommend that
attempts be made to encourage and suppbrt their R&D efforts.
Considering new entries into the pesticide research field, we expect
few new entries, not as many as there will be dropouts of both small and
large companies. One reason for the lack of new entries is that it requires
a minimum of about 10 years of investment, before any product can be
brought to registration, and hence marketing. There are few companies
willing to make this type of investment in a highly regulated, highly
risky business. New entries will most likely result from joint ventures
with foreign companies already in the business elsewhere, where a substantive
base of R&D and marketing already exists, or from expansion of companies
such as the pharmaceutical companies, who are experienced in a regulated
industry, and have many of the requisite skills in chemistry, biology,
needed facilities, and capital. The trends for moving into the herbicide
business from insecticide business will probably continue, because of
the larger markets and greater volume of products. Several of the larger
companies we contacted indicated that their managements would, under today's
conditions, be opposed to their new entry into the pesticide business,
primarily because of the greater opportunities for growth and return on
investment in other sectors of the chemical business. Most major chemical
and oil companies will continue to avoid the biological control area because
of the risk involved, the unfamiliarity with the products, the general small
volume of production, and other desire to remain a chemical company. The
innovative work in this area will probably be left to smaller companies
and federally supported efforts.
7. Differences in Responses Among Industry Staff
During this program, we discussed the impact of current regulations on
pesticide research and development with several different categories of
industry staff—those involved in pesticide research, marketing, management,
regulatory liaison, and finance. Although many comments from these diverse
representatives were similar in nature and viewpoint, and to some extent
represented a company or industry-wide position, some differences in their
response was noted.
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Those involved in corporate management and finance were specifically
concerned with the increased cost and development time that might result
from FEPCA implementation. Increased cost and development time could
significantly affect the risk, rate of return, and profitability of the
pesticide segment of the corporation. This in turn could change its
internal competitive position with relation to other parts of the corpora-
tion, and affect managements' decisions on the viability of the pesticide
segment and their commitment of resources and other support to this segment.
Corporate and financial management staff were equally concerned with other
EPA regulations—water, air and solid waste—and OSHA regulations and their
effect on the future of pesticide business.
Marketing specialists were specifically concerned with the time
Increases in the registration process and the lack of awareness of seasonal
effects in the industry. Delay of one or more growing seasons in the
registration of a new product or use of an old product was of importance
because of the implications on the marketing organization and the loss of
competitive advantage over other companies. The classification system for
restricted use pesticides, and certification of applicators, were mentioned
by marketing staff as significant sections of FEPCA which affect pesticide
markets and have a secondary impact on R&D. The experimental use permit
program as first proposed by EPA was criticized heavily by marketing staff
because of their previous practice of obtaining much of the efficacy and
acceptance data needed to develop marketing strategy from a somewhat loosely
controlled experimental permit program.
Research and development staff generally felt that FEPCA implementation
did not have a direct impact on the level of work they conducted. However,
they felt that implementation of FEPCA would reduce the emphasis and
support resources made available to them to do innovative work—to develop
new innovative pest control approaches. Their efforts would be expanded
in additional test work, support of existing registrations, and other
defensive research. As a result, the opportunities to develop, and ultimately
market, new pesticides would be significantly reduced. Research and develop-
ment staff are becoming more aware of concerns of marketing and management
staff, since the reduction of resources will affect the direction of their
efforts.
8. Biological Control Approaches
In Chaper III the current trends in R&D activity in biological control
approaches was discussed. It was pointed out that the major pesticide
developers are not pursuing active R&D programs for most biological control
approaches, other than plant or insect growth regulators and juvenile
hormones (the 'synthetic' biological controls) because of a variety of
reasons, most of which have little to do with legislative or regulatory
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action. There are, however, some positive and negative impacts of the
regulations on R&D activities in biological controls which should be
mentioned.
Those who are active in the development of biological control approaches,
primarily BT, viruses, pheromones, etc., feel that some of the data require-
ments for registration are unreasonable. They point out that, in some
cases, very small amounts of these materials are used in practical application,
yet larger quantities must be synthesized and produced only for the tests
required for registration, i.e., toxicity, residue, environmental degradation,
etc. With the small amounts used, environmental effects, in some cases,
become meaningless* Developers believe that a reduced set of test require-
ments are needed for biological control approaches. (We understand that
guidelines for the registration of biological controls are being established.)
Of course, those who develop conventional pesticides believe that biological
control products should be subjected to the same tests and examined with
even more caution because of the general lack of knowledge on their behavior.
As mentioned earlier, there are no direct patent benefits for bacteria
or viruses used as pesticide. Industry hopes that section 3(c)(1)(D) can
be used to some degree to provide a type of protection to those who develop
data needed for registration of biological control pesticides.
The limitations imposed by experimental use permits are believed by
industry to restrict R&D in biological control approaches. Large land
areas may be needed for effective testing of biological control methods,
and several companies feel that this will not be possible under the new
experimental use permit system.
The problem of delays, serial data demands, etc., are all mentioned
as effects of the current regulations which impact biological control
R&D, but technical problems still occupy most of the efforts of the
developers.
It is the feeling of those who promote biological controls, that
although the law recognizes that these types of innovative approaches
should be encouraged, the regulations to date do not encourage their
development. However, even if there were special provisions of the
regulations to encourage the development of biological controls, it is
doubtful that many more companies would participate actively in this R&D
effort because of the acceptance, economic, and risk factors mentioned
in Section 111. Most likely biological control approaches will have to
be government supported and/or subsidized within industry to make
reasonable progress in today's economic climate.
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E. BENEFITS
Most of the discussion so far has focused on negative impacts of the
changes in legislation. Positive impacts will occur also, both in regard
to R&D and in regard to society in general. Some of the benefits to
R&D are as follows:
1.	The increase data requirements and the resulting increase in
cost have led to a reduction in the number of compounds being put through
the R&D process. This in turn has led to a more efficient selection of
compounds chosen as potentially successful. Earlier decision making,
with increased input from a variety of research areas, decreases risk by
decreasing the number of compounds being put through the extensive testing
necessary for registration.
2.	The need to improve the success to failure ratio also increases
the emphasis placed on the directed approach to synthesis and screening,
i.e., screening compounds specifically synthesized for pesticidal activity.
While presently this approach concentrates on compounds related to existing
pesticides, it will allow opportunity for basic biochemical research to
direct the synthesis, and thus the development of innovative pesticides
based on new modes of action.
3.	Ten years ago, the regulatory liaison personnel had to maintain
contact with two agencies - FDA and USDA and also anticipate the comments
from the Department of Interior and the Department of Health, Education
and Welfare. One of the benefits of FEPCA is that present legislation
necessitates liaison with only one agency.
4.	The increase in data requirements has resulted in better analysis
and test methods used for analysis. This increase in sophistication in
methods and equipment has resulted in better data and a better under-
standing of both the mechanisms of pesticide action and the environmental
and safety effects of pesticide products.
5.	Ultimately the increased amount of data which will be used by
EPA to make decisions in registrations, will result in better decisions
balancing efficacy and environmental and safety impact and an overall
decrease in adverse environmental impact.
6.	The certified applicator program will result in two beneficial
impacts. First, there will be an elimination of "overkill" in the
application of pesticide, i.e., the practice by individual farmers of
applying more pesticide than the label recommends in order to assure
efficacy. This practice is not as widespread now as in previous years
during the introduction of many new pesticides on the market. Additionally,
there will be a general upgrading of knowledge concerning the proper use
of pesticides by certified applicators and by the state organizations which
must certify them. State knowledge of pesticide use and its effects will
also increase greatly in those states which accept responsibility for the
registration of pesticides.
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V. RECOMMENDATIONS TO REDUCE ADVERSE EFFECTS
OF FEPCA IMPLEMENTATION
In our discussions with representatives of the pesticide industry,
a number of specific recommendations were presented to us on methods by
which adverse impacts of FEPCA implementation could be mitigated. Some
of these involved specific changes to the regulations which have been
proposed and published in the Federal Register; other involved general
procedural approaches which EPA could follow, and still others dealt with
incentives that could be offered to promote research and development
activities. In addition, we have developed some recommendations based
upon information received from industry contacts, our review of the literature,
and data on the research and development activities of industry. We do
not believe it is appropriate to report all the comments provided by
industry in response to publications in the Federal Register on specific
proposed regulations. These are a matter of public record. Rather we will
present briefly a series of recommendations relating to procedures and
policies, research activities and incentives programs to be considered by
EPA which may expedite and encourage research and development activities
by industry and promote the development of safe, effective and environmentally
acceptable pesticides.
Procedures and Policies
• Policies and procedures for enhancing the registration/review
process at EPA should be considered Including:
Publish complete guidelines for registration applicants,
including definitive test requirements, acceptable test
procedures, criteria for acceptance of data, acceptable
levels of safety and environmental impact, etc. The
guidelines must be sufficiently flexible to cover all
products and uses, including biological control and other
innovative approaches, and have specific procedures for
registration for pesticide mixtures, amendments to
labeling, new crop additions, etc.
Develop procedures for updating registration guidelines
at defined intervals with advance or concurrent notification
of potential registrants of any changes between updates.
Announce and adhere to definitive schedules for the
registration review process, with provisions for
scheduled periodic (or interim) formal and informal
communications with the registrant to convey additional
information or requirements, to discuss results, and
promote timely resubmissions, if required. Review
schedules should consider the seasonal nature of research
and development activities as well as pesticide marketing.
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Modify the procedures for submission of information under
Section 3(c)(1)(D) to make it more relevant to the specific
company situations.
Develop procedures to promote internal consistency in the
review process in terms of data acceptability, communications,
comments, etc. with individual reviewers able to communicate
questions of the applicant as soon as they are raised.
•	Policies and procedures be considered for expanding and diversi-
fying the EPA Pesticide Registration Staff including:
Increase GS ratings and pay levels to provide for advance-
ment of existing staff and recruitment of new staff
experienced in agriculture, pesticide development, health
and safety, biological controls, and environmental effects.
Develop programs for internship/work/study of selected
registration division staff at USDA, universities, and
industry to gain experience in all phases of the pesticide
research development process.
Develop an EPA/industry/university interchange program to
provide and gain special expertise in diverse fields needed
in the registration process, such as biological controls, etc.
-	Provide for flexibility in number and experience of registra-
tion staff in periods of seasonal load.
•	Policies and procedures be considered for improving intra- and
interagency' communication, liaison and cooperation including:
-	Increased interaction between OPP Criteria and Evaluation
Division and Registration Division.
Increased interaction, information exchange and use of
staff in EPA regional offices.
Increased interaction with USDA research staff to stimulate
needed research.
4
Increased interaction and liaison with state environmental
and health agencies, pesticide control boards, etc., to
enhance states ability to issue experimental permits,
certify applicators and register pesticides for local
use, to control disposal of containers, etc., and to
provide for uniformity among state programs.
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•	Policies and procedures be considered for enhancing the utility
and ease of Implementation of experimental use permit and similar
limited use programs, including:
Use of registration divisionstaff for periodic monitoring
of field programs under experimental use permit system.
Adopt a co-minitor program for evaluation and monitoring of
field studies using registration branch and regional office
staff.
Develop an alternative approach to the current experimental
use permit system which allows for limited sale of pesticides
under provisional registration, possibly requiring application
by certified applicators, with sufficient restrictions to
insure public safety and environmental protection, with
submission of data to EPA during the provisional registration
period before full registration is granted.
Develop an approach whereby distributors and dealers can
participate in any experimental use permit system.
Research Activities
•	Conduct cost/benefit analyses relating to decisions and criteria
for acceptance of toxicity and environmental impact data for
product registration, suspension, and cancellation of pesticides.
•	Conduct basic biochemical studies to elucidate mechanisms of
pest control and enhance the development of new approaches to
pest control.
•	Develop approaches to improve consumer acceptance of biological
control methods.
•	Conduct research on interaction of synergism in pesticide
mixtures to determine the requirements for tests on mixtures.
•	Conduct research on methods of pesticide and container disposal.
•	Support basic research in biological control mechanisms, including
stabilization of viruses and biological methods of application,
isolation, purification, etc.
•	Support research on pesticides for use with minor crops.
•	Support research on toxicology and environmental effects
related to classes of chemicals and biologicals in common use
and expected development.
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Incentive Programs
•	Develop programs of incentives for industry, and universities,
to stimulate and encourage research and development on:
Innovative pest control methods
Pesticides for minor uses
These incentives programs might include: patents or other
protection for bacterial or viral strains, loan system for
specific research and development steps with payback provisions,
purchase of crops for destruction in field tests.
•	Develop internal incentives for EPA staff to adhere to registration
schedules, policies and practice and to encourage registration of
safe and effective pesticides.
•	Consider incentives for complete pest control programs and the
total service concept for agriculture.
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VI. CONCLUSIONS
The major conclusions developed In this study are:
1.	Over the past 25 years, pesticide regulations have increased
slowly and steadily in breadth and depth; their Impact on innovative
research and development in industry has increased in parallel. Major
impacts on research and development activities occurred in 1966-1967
as a result of the requirements for finite tolerances and in 1970 as
a result of additional environmental data requirements. Implementation
of FEPCA will result in additional impacts on specific portions of the
R&D process, but will not result in drastic changes in innovative activity.
Legislation and regulations have an impact on R&D; the procedural aspects
°f implementation of these regulations have a major impact on the total
pesticide development process.
2.	The principal Impacts of the steady growth in regulatory action
on pesticide research and development activities are:
•	a substantial increase in the time required for development
of a pesticide from synthesis through registration
•	a substantial increase in the cost to develop and register
individual pesticides
•	an increased quantity and quality of data on the use, application,
safety and environmental effects of pesticides
•	increased risk for the developer because of uncertainty of the
timing and extent of return on the R&D investment
•	increased allocation of R&D resources to the defense and
maintenance of existing product lines and extension of pesticides
to new uses at the expense of decrease in innovative R&D
•	a reordering of the timing of specific R&D activities and
reallocation of some R&D manpower resources
•	increased use of outside resources to conduct portions of the
R&D process for the pesticide Industry
•	increased emphasis on products which Involve foreign markets
in order to increase volume sales
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3.	The principal aspects of the implementation of FEPCA which will
have the most effect on pesticide R&D are continued increases in
environmental data requirements and their uncertainty, and the implementation
of the experimental use permit system. Increased R&D costs, lengthening
and reordering of the R&D tasks, and shifts of resources to extending product
lines are the most important changes anticipated. Only minor impacts on
R&D activities are anticipated from regulatory provisions dealing with
certified applicators, restricted use designation, rights to data and
compensation for data, packaging, disposal, etc.
4.	The principal impacts of pesticide regulation on future pesticide
products are:
•	continued development of herbicides and other potentially
high volume/profit compounds
•	continued emphasis on products for major agricultural crops
with decreasing emphasis on products for minor crops
•	continued decrease in the number of new pesticide compounds
which enter the marketplace, resulting from increased
costs per compound in the development phase.
5.	The principal decision-making factors in the R&D process for
proceeding with the development of a specific pesticide are, in order of
importance: efficacy, projected cost compared to competitive products,
anticipated sales volume and profitability, human safety (toxicity), and
environmental impact. Although the recent regulations may eventually
increase the importance of environmental impact as a decision-making factor,
the other factors remain more important in determining which potential
products will reach the marketplace.
6.	The large established multi-product diversified pesticide developer
will continue to be the major source of R&D effort in industry, and will
continue to develop and market new products with minimum impact of
regulations. The smaller and more recently formed companies, which have
only few viable products to use as a basis for research commitment, may
not be able to sustain the increases in R&D costs and extended product
development time. They will either withdraw from the R&D function, be
consolidated with larger companies, or withdraw from the marketplace.
Increased costs from regulatory action will hasten this process. Unfortun-
ately many of the smaller and more recently formed companies have a greater
capacity and ability for innovative research than other firms since they
are less chemically oriented and less oriented toward large volume sales.
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