Use
of Biosolids Incinerator Ash as a Phosphorus Source for Turfgrass
Introduction
This
experiment was conducted to investigate the use of biosolids incinerator
ash from the Allegheny County Sanitary Authority (ALCOSAN) as a phosphorus (P) source for turfgrass soils. Biosolids
incinerator ash is a dry, powdery, mineral material that consists mostly of
silt sized grains. Organic material, organic chemicals, and all microbes in the
original biosolids are incinerated. Inorganic constituents of the original biosolids
are concentrated in the ash. The ash contains 4 - 5% total P and therefore has
potential value as a source of P for plant nutrition.
We
conducted a field experiment to determine if biosolids incinerator ash is an effective
source of P for turfgrass, and to determine if the ash could be beneficially used
as a component of manufactured topsoil for landscaping. Major environmental concerns
with this use of biosolids incinerator ash include determining appropriate ash
addition rates to avoid excessive P loading and potential P runoff or leaching,
and loading and availability of trace elements.
In
preliminary laboratory work we combined incinerator ash or triple super phosphate
(TSP) fertilizer with a low P-test soil on the basis of the total amount of P
added. Rates of P addition ranged from 0 to 140 mg P/kg soil. We incubated the
mixtures at room temperature and allowed them to run through several wetting and
drying cycles. Bray P1 extractable P was determined on the mixtures. Results of
the incubation are shown below.
These
data indicate that TSP fertilizer is approximately four times more effective than
the biosolids ash at increasing the Bray P1 soil test. This indicates the P in
the ash is far less soluble than the P in TSP.
Based
on these results we established a field experiment to investigate turfgrass response
to blending ash with soil on a P basis. Using a low P topsoil material we combined
ash with soil at rates of 0, 0.9, 1.8, and 3.6 % on a dry weight basis. Based
on the incubation study, these rates of addition should be equivalent to 0, 0.5,
1.0, and 2.0 times the amount of P needed to increase soil test P to recommended
levels for turf.
Trace
element concentrations in the ash are given below. At the 1.8% rate of ash addition
to soil, calculated total trace element addition to the soil is shown below and
compared to the regulatory cumulative pollutant loading limit (CPLR) for biosolids
application.
Field
Experiment Setup
The
field experiment consisted of 5 treatments. The topsoil with no amendment (control),
topsoil with recommended TSP fertilizer, and ash mixed with topsoil at rates equivalent
to 0.5, 1.0, and 2.0 times the amount of P added with TSP fertilizer. Screened
soil and ash were blended at these rates on a weight basis. Soil/ash blends where
placed in 10' x10' plots which were approximately 10" deep and were arranged
in 3 randomized complete blocks. Plots were staked and separated by silt fence.
Volume of soil needed to fill one plot was placed in a soil shredder along with
the needed weight of ash to achieve the desired mix ratio. Soil and ash were thoroughly
mixed in the shredder, fed into a dump truck, and dumped in the appropriate field
plot. Mixed soil was evenly spread over the plot using hand shovels and rakes.
The TSP fertilizer (3.3 lb/plot) and muriate of potash (KCl) fertilizer (0.5 lb/plot)
was spread on the surface of TSP treatment plots and mixed into the soil using
hand shovels and rakes. All plots received surface application of urea (0.5 lb/plot)
and ground agricultural limestone (6.3 lb/plot). These materials were incorporated
by hand using shovels and rakes. The entire plot area was broadcast seeded with
5.5 lb of perennial ryegrass seed (Lolium perenne, L.) followed by a light raking
and mulched with clean wheat straw. The plots were watered as needed to maintain
growth of ryegrass.


Partially
constructed plots (made from silt fence) |

Installing
cap ends of plots |

Filling
buckets with incinerated ash |

Weighing
ash that will be added to soil |

Adding
soil and ash to mixer |

Overview
of site |

Blended
soil is fed onto dumptruck |

Control
soil plots are filled |

Other
plots with amendments are filled by dumptruck |

First
row of plots filled |

Another
plot filled |

Each
plot is raked even |

Second
row almost filled |

All
plots filled |

Fertilizer
and lime applied to each plot |

Hand
incorporation of surface amendments |

Plot
seeding and mulching |

Finished
beds. Soil samples being taken |
Following
a six week establishment period, the ryegrass was mowed approximately once per
week until fall growth ended. Plots were again mowed once each week when growth
resumed in the spring of 2003. On alternate mowing dates the ryegrass growth on
each plot was sampled for yield determination and tissue analysis. Sampling dates
in Fall 2002 were 9/24, 10/10, 10/24 and 11/8; and in Spring 2003 were 5/2, 5/16,
5/30, 6/13, and 7/2. Sampling was done using a modified rear discharge bagging
mower that blew grass clippings into mesh filter bags. Plot boundaries were first
mowed and samples for yield measurement and tissue analysis were collected by
mowing a single pass across each plot. Length and width of the sampled area was
measured. Clippings were dried for 48 hours at 65ºC and weighed. Two 10 g
composite samples for each plot, representing fall 2002 and spring 2003 samples,
were made by mixing tissue material from each harvest in ratios based on contribution
of each cutting to total yield. Composite tissue samples were analyzed at the
Penn State University Ag Analytical Services Lab for N, P, K, Ca, Mg, Al, Mn,
Fe, B, Cd, Co, Cu, Mo, Na, Ni, Pb, and Zn. Spring 2003 composite samples were
also analyzed for As, Se, and Hg.

Emerging
seedlings |

Another
view |

Some
plot differences already evident |
During
the fall of 2002 and spring/summer of 2003, grass growth, grass nutrients and
trace element content were measured. We conducted soil tests to determine soil
test P response and total trace element concentrations.

Mowing
plot edges prior to harvest |

Plot
edges mown |

Measuring
harvest plot length |

Harvested
plots |

Another
view of harvested plots |

Some
plot differences already evident |
Results and discussion
Soil phosphorus (P)
ALCOSAN biosolids incinerator ash was effective at increasing Mehlich3 P levels (Figure 6). Increasing amounts of ash resulted in linear increases in soil P and there was very little decay in soil P levels during the experiment. By contrast, soil test P levels were initially much higher with trisodium phosphate (TSP) fertilizer than with ash and then decreased substantially within 3 months. This result reflects the much more soluble nature of P in TSP than in ash. The first soil samples were collected immediately after treatment application, before there was any opportunity for TSP fertilizer granules to dissolve and react with the soil. During the next 3 months soil test P decreased substantially in the TSP treatment, presumably a result of soluble P reaction with, and strong sorption on, soil constituents. Mehlich3 P levels with TSP and the 1x ash application rate remained similar throughout the experiment. The total amount of P applied in the 1 x ash rate was 4.1 times greater than the total amount of P applied in the TSP. This result substantiates the preliminary incubation study that indicated ash P was approximately 25% as effective as TSP at increasing soil test P levels. These results indicate that about 75% of the P in biosolids incinerator ash is highly insoluble and is unlikely to be available for plant uptake. For more information download the entire final report as a PDF document.

Figure 6. Effect of ash addition on Mehlich3 extractable soil phosphorus.
Rye Grass Yield
Fall establishment and growth of ryegrass was improved by ash addition. Visual observation of the plots indicated turf establishment, density, and color was poorer in control plots than in all other treatments (see picture below, control plot is in lower left corner).
Such differences were no longer visible in Spring 2003 when growth on all plots was more vigorous and turf density was greater than in the previous fall (see picture below, control plot is in lower left corner).
Dry matter production by ryegrass increased with increasing ash addition in Fall 2002 (see graph below). Ash was equally effective as TSP fertilizer at stimulating turf establishment and early growth of ryegrass. Increased ryegrass growth with ash application was apparently due to increased P availability. For more information download the entire final report as a PDF document.
Tissue phosphorus concentrations
Tissue phosphorus concentrations were increased by ash in the fall of 2002 with much smaller increases in spring 2003 (see graph below). Lower overall P concentrations in spring 2003 tissue reflects the diluting effect of greater dry matter production and possibly reduced availability of soil P in the spring of 2003. Again, ash was equally effective as TSP in providing P for turf growth. For more information download the entire final report as a PDF document.
Work was
completed in the Summer of 2003.
Click here for an executive summary.
Click here for the Final
report.
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