II. R&D NEEDS AND POTENTIAL PROJECTS
D. Cyanide
1. Background
Free cyanide is a highly toxic chemical that is found in the environment
at low concentrations coming from natural sources. It reaches
toxic levels mostly through industrial processes such as mineral
processing, electroplating, and paper-making. The Resource Conservation
and Recovery Act ban on land disposal of solid waste containing
cyanides poses a major waste management problem for industries
using cyanide in their processes.
Cyanide is also a regulatory target because of its toxicity, incompatibility
with most publicly-owned treatment plants, and danger to sewer
workers and marine life. EPA has imposed limits on the quantity
of cyanide in both the treated wastewater that is discharged to
sewers and rivers and on any residuals from metal finishing operations
(sludges, filters, filter cakes, spent solutions, etc.). A variety
of electroplating and metal finishing waste streams contain metal-cyanide
complexes. Metal-cyanide complexes formed in these industries
include metals such as iron, nickel, zinc, cobalt, cadmium, copper,
mercury, and precious metals (silver, gold, platinum).
There is some free cyanide found in electroplating wastewater
from cyanide-based plating chemistries; it is one of the most
toxic contaminants in the wastewater. Evaporation, while effective,
has high energy costs. The commonly used cyanide destruction
techniques, such as treatment with oxidizers, do not easily destroy
all the cyanide. For example, iron, cobalt, and nickel cyanides
are not affected by basic hypochlorite treatment and are often
precipitated out into the sludge that is formed under the process.
Thus, elevated levels (up to 5,000 ppm, or 0.5%) of complexed
cyanide typically appear in hydroxide-precipitated, heavy-metal
sludges produced during the treatment of many electroplating wastewater
solutions
From an environmental perspective, cyanide-bearing processing
solutions should be operated in a completely closed loop, if possible.
When not possible, wastes and wastewater bearing highly toxic
forms of cyanide should be detoxified to a level acceptable to
the environment in which those cyanides are released.
While great strides are being made to create plating processes
that do not require cyanides, there are some notable plating solutions
available now without such substitutes. Examples include silver,
brass, bronze, and Alballoy (an alloy of copper, zinc, and tin).
Furthermore, some non-cyanide replacements for conventional plating
processes have proven to be limited in application--e.g., non-cyanide
cadmium, non-cyanide silver/brass, non-cyanide (sulfate) gold,
and non-cyanide copper. One example of a successful non-cyanide
bath is non-cyanide zinc; over the last thirty years it has replaced
about 70 percent of cyanide zinc and this percentage could easily
go higher.
2. Federal Survey
A surprising result of reviewing the sources for recent and ongoing
R&D was the paucity of governmental funding for development
and demonstration of alternatives to or recovery of cyanide.
Only three studies were found, totaling $207K. EPA has supported
two demonstration projects showing ZnCl as a substitute for ZnCN
and CdCN baths; DOD is supporting work to develop a noncyanide-based
stripping solution. The AESF Research Board is currently supporting
a project investigating non-cyanide copper plating alternatives
at North Carolina State University.
3. Projects
Various projects warrant investigation.
a. Study the optimization of existing baths for recovery and recycle
of cyanide-containing solutions and chemicals. Drag-out tanks
are often the simplest and least expensive method of recovery.
b. Evaluate polymer filtration for recovery and recycle.
c. Evaluate substitute baths as they enter the market--e.g., as
used on zinc-based die castings.
d. Contributors to this Plan often voiced concern that there is
not enough data or risk characterization to support regulations.
More research is needed to help establish risk levels; better
understanding of risks imposed by emissions would help prioritize
future R&D projects.
e. Develop improved analytical procedures for total and especially
amenable cyanide in water and solid wastes.
f. Determine whether complexed cyanide in F-006 wastes meet Hazardous
Waste Identification Rule (HWIR) II delisting requirements.
g. Investigate the environmental impact of complexed cyanide in
F-006 waste under present stabilization/disposal practices.
i. Develop low-cyanide process solutions.
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