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Compared to new plants, older facilities tend to have a greater volume of wastewater and higher pollutant loadings, even though pollutant concentrations may be lower due to water contributions from noncontact sources. EPA also requested that pesticide manufacturing facilities submit wastewater self-monitoring data. Twenty-five of the 29 PAIs tested exhibited some adsorption capacity.

While many plants provide extensive treatment to remove PAls, priority pollutants, and other pollutants, some plants provide no treatment. The oldest reported pesticide operation began inwhile the most recent operation began in Unlike priority pollutants, PAIs detected in commingled wastewaters could be attributed to the pesticide processes since other industrial production at the facility would not generate wastewaters containing PAIs.

These data usually matched well with the facility’s indication in the Facility Census that the pollutant was known or believed present in their pesticide process wastewaters. This factor is directly related to the product type and raw materials used, and therefore is consistent with subcategorization datashret on product type and raw materials.

The dayasheet study was conducted at three chlorine dosages at three different contact times. This source does not include any production information and is publicly available. The priority pollutant characterization data presented in this section for organic and metallo-organic pesticide process wastewaters were used by EPA to evaluate which priority pollutants should be regulated.

See “Economic Impact Analysis of Effluent Limitations and Standards for the Pesticide Manufacturers” d7l03 information concerning the development of the economic portion of the questionnaire. If an automatic sampler could not be used, dataasheet equal volume grab datasheey, or aliquots, were manually collected at equal time datashert and added to the compositing container a specially clean liter glass jar. After the individual sample fraction containers were filled each day, they were preserved according to EPA protocol.


Acid and basic reagents are used to facilitate, catalyze, or participate in the reaction process.

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Herbicide production in increased rapidly through the fall and early winter and peaked in March of that year, just prior to the growing season. Overall, EPA does not believe that plant size is an appropriate method of subcategorization for the pesticide chemicals manufacturing industry.

In addition to other factors specified in Section b 4 Bthe Act requires that BCT limitations be established in light of a two part “cost-reasonableness” test.

In addition to reporting priority pollutants in the Facility Census, some facilities also submitted priority pollutant data obtained during self-monitoring sampling.

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The ACT data from both tests were comparable to the full-scale system data with respect to carbon usage and carbon loading. See Table for contaminated stormwater reported as another pesticide wastewater source. The economic portion was subsequently revised, resubmitted and cleared. They do attempt to present a general mechanism for the majority of pesticide active ingredients produced within each category. Results of these data gathering efforts are described in more detail below.

A summary of the pesticide active ingredients considered for regulation, their production levels, and production distribution is presented below.

In cases where treatability studies did not contain sufficient information to determine process variability, daily and monthly variability were based on the performance datasheft operating BAT treatment systems. In the membrane filtration treatability study, a series of bench-scale tests were conducted to identify specific PAIs which could be separated from water by various membrane materials.

Because treatability data were lacking for some PAIs, individual PAIs, which were expected to be treatable with a specific technology, were targeted for treatability studies.

Short-term sampling data collected during site visits by EPA to pesticide manufacturing plants between and were also reviewed dp703 considered by the Agency. The two subcategories are the same cl703 the manufacturing subcategories contained in the existing 40 CFR Part regulations. These sources are described in more detail below.

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Each formulation has a distinct registration. For example, carbon adsorption may remove dp703 which would be toxic to a downstream biological treatment system. BAT may Include process changes or internal satasheet, even when these technologies are not common industry practice.


On January 2,EPA published an Effluent Guidelines Plan 55 FR 80in which schedules were established for developing new and revised effluent guidelines for several industry categories.

The proposed standards would apply to all existing indirect discharging organic pesticide chemicals manufacturing plants. The reaction for Nabam using ethylenediamine is shown in Figure This section presents information on water use at these 90 facilities. When the cost of controlling those volatile toxic pollutants is added to the cost of alkaline chlorination, the total cost for chlorination may exceed the cost of ozone oxidation.

The aryl N-methylcarbamates are easily formed when phenol and methyl isocyanate are reacted. Also, older facilities that have continued to manufacture the same product have often improved or modified the process and treatment technologies over time. However, both of these dl7033 are a result of individual facility practices, rather than a trend of different segments of the industry. The impact darasheet solid waste disposal is dependent datashdet the treatment technology employed by a facility and the quantity and quality of solid waste generated by that facility.

The responses in many cases indicated that the facility did not manufacture PAIs anymore and in some cases indicated that the facility was closed. This parameter can vary widely from plant to plant and can also show extreme variations in a single plant’s raw wastewater, depending on such factors dattasheet waste concentration and the portion of the process cycle discharging at the time of measurement.

datashset All of the PAIs selected were expected to hydrolyze under some conditions. Where existing performance is uniformly inadequate, BPT may be transferred from a different subcategory or category. Contaminated stormwater reported as a source of process wastewater is presented here. The half life ranged from 0. Liquid and solid wastes include hazardous and nonhazardous organic and inorganic wastes as well as wastewater.

EPA estimates that approximately 2. In addition, organo-tin pesticides were datazheet covered by BPT.