> Fertilization
Environmental protection
A person who uses fertilizer must store, handle and apply
the fertilizer in a manner that protects forest resources.
No fertilizer application zone
A 10-metre "no fertilizer application
zone" or buffer zone should be left around the following
water bodies:
- a fisheries lake
- any designated fishery stream (S1-S4)*
- a stream that can be identified, on
a pre-flight inspection, as one observable as open water
that flows into any designated fishery stream (S5, S6).*
* Riparian classes are defined in Part 10 of the Operational
Planning Regulation.
A typical swath width for helicopter aerial fertilization
is approximately 60 m. Fertilizer is spread 30 m on each
side of the helicopter. In this case a flight parallel
to the water body should have the helicopter 40 m away
to maintain a 10-metre buffer strip.
In community watersheds the following buffers are required:
- 10 m around a flowing stream that
is observable from the air
- 100 m upstream and upslope of a community
watershed intake.
Storage and handling of fertilizer
A material safety data sheet for each
type of fertilizer should be reviewed by all personnel
involved in the fertilization project. These sheets must
be kept on site. The data sheet lists preventive and corrective
measures for storage and worker safety.
Storage
Forest grade urea is not a controlled
product under WHMIS (Workplace Hazardous Material Information
System) or regulated for rail or road transportation.
Because of its solubility in water, however, urea must
be stored in dry containers and protected from moisture.
Urea is hydrophilic and moisture will make the product
go lumpy.
Security of a storage area is important to prevent cattle
and wildlife from consuming urea, preventing unauthorized
removal of fertilizer, and protecting equipment from vandalism.
A night watchman or other method of security, such as
fencing may be used.
Contingency plan
Prior to commencement of projects, a
contingency plan must be in place, in case of accidental
spills of fertilizer.
For areas inside community watersheds the contingency
plan must include measures to ensure that water quality
is maintained. The contents of the plan include, but are
not limited to, the following guidelines:
- names and telephone numbers of emergency
- plan for an alternate water supply
until levels return to normal. The need for alternate
supplies will be determined by the medical health officer
- water quality monitoring program to
document water quality returning to background, or to
a level acceptable by the Ministry of Health
- accident clean up procedures, including
remediation of the site and disposal of spill material.
The spill contingency plan should be carried in designated
vehicles.
Protection of water resource
Nutrients from forest fertilizer applications can enter
water bodies through leaching, runoff, or directly when
fertilizers are applied aerially. Sensitive areas are
protected using buffers and limiting the area receiving
the fertilizer treatment.
Community watersheds
Up to 30% of a community watershed can normally be fertilized
in any 12-month period. If buffer zones cannot be maintained
around at least 75% of the total length of flowing streams
then a maximum of 12% of the watershed can be fertilized
in a 12-month period.
Do not fertilize in community watersheds if waterbodies
contain high chlorophyll levels. Check waterbodies for
presence of clumps or strings of periphyton (algae) attached
to large stones or aquatic plants. Periphyton strings
greater than 3-5 centimetres are indicative of high chlorophyll
levels. Such waterbodies may exceed the chlorophyll limits
for community watersheds. Sampling for chlorophyll should
not be necessary if care is taken to visually assess the
presence of periphyton. Sampling procedures for periphyton
are contained in the Biological Sampling Manual,
B.C. Ministry of Environment, Lands and Parks, Water Quality
Branch. High levels of periphyton can be caused by excess
nutrients in the water or the absence of benthic organisms
that feed on the algae.
Fertilization in community watersheds must ensure
that
(a) the fertilizer is not applied
(i) closer than
100 m upslope of a water intake, or
(ii) within
10 m of a perennial stream that is observable from the
air, at the height the fertilizer will be applied, unless
otherwise authorized by both the district manager and
the Minister of Health, and
(b) the application of nitrogen fertilizer does not cause
(i) nitrate
nitrogen levels in a stream to exceed 10 ppm measured
immediately below the area where the fertilizer is applied,
(ii) chlorophyll
levels in a stream to exceed
(A) 2 micrograms/litre
in a lake, or
(B) 5 milligrams/square
metre in a stream, or
(iii) water quality to fall below any water quality objectives
or criteria approved by the Minister of Environment, Lands
and Parks
In community watersheds with lakes or
reservoirs, do not apply fertilizer during times of rising
water temperatures. Generally, do not apply fertilizer
during the following periods:
- May 15-September 15 (Interior: former
Cariboo, Prince George, and Prince Rupert Regions)
- April 15-September 15 (Interior: former
Kamloops and Nelson Regions)
In addition to guidance here, special requirements are
needed for fertilizer application in community watersheds.
Refer to the Community Watershed Guidebook: Forest
Fertilizers.
Fisheries resources
Sensitive aquatic environments that are
important for supporting various life history stages of
fish must be protected from the direct toxic effects of
fertilizer elements (e.g., ammonia, nitrite-N), and indirect
effects due to eutrophication. In extreme situations,
the eutrophication resulting from excess runoff of fertilizer
can lead to a reduction in critical levels of dissolved
oxygen necessary to sustain aquatic life, and can cause
other habitat impacts. Fisheries-sensitive areas can include
fish-bearing streams, tributaries that flow into fish-bearing
streams, ephemeral watercourses and flood channels, swamps,
seasonally flooded depressions, lake spawning areas, or
estuaries.
Protection for these sensitive areas has been provided
principally through the use of 10-m buffer zones. Fisheries-sensitive
areas containing significant numbers of streams that cannot
be seen from the air are not appropriate for aerial fertilization.
Streams which are not visible from the air cannot practically
be buffered.
Cattle and wildlife
Three aspects should be considered with
regard to wildlife when applying fertilizer: the availability,
palatability, and inherent toxicity of the applied fertilizer.
Urea applied to forest soil as pellets is available to
wildlife for a period of a few hours to a few days, depending
mainly on precipitation patterns after fertilization.
Although small mammals and birds quickly lose interest
in the urea pellets, larger wildlife and domestic cattle
are attracted to it. Small doses (a few handfuls) of urea
are lethal to these animals.
In range use areas, arrange with the range resource officer
to have cattle off the site during treatment. It is improbable
that cattle will ingest a lethal dose from a properly
spread fertilizer application within the block or from
compacted surfaces such as roads or landings. However,
cattle are attracted to urea and will even make holes
in unopened bags. Therefore, do not leave fertilizer stores
unattended on a site if cattle are expected to be in the
area.
Daily clean up is required of loading sites to prevent
fertilizer being ingested by animals.
Water quality sampling
Water quality sampling is required in
community watersheds and should be done when fertilizing
near fisheries-sensitive zones. Samples should be taken
before, during, and after treatment. Guidelines for sampling
and analysis are provided in http://www.for.gov.bc.ca/tasb/legsregs/fpc/fpcguide/fert/app4.htm