18-Env-B6 Agricultural Waste Management · December 2018
Nivaar worked solution (AI-drafted; not reviewed by a licensed engineer)
National Exams, December 2018 — 18-Env-B6, Agricultural Waste Management (3 hours, open book, all 15 questions to be attempted, 100 marks total).
Reference texts: Rynk et al., On-Farm Composting Handbook (NRAES-54); OMAFRA, Nutrient Management Act, 2002 and O. Reg. 267/03 / Nutrient Management Protocol (NMAN); Metcalf & Eddy, Wastewater Engineering (anaerobic digestion chapter); ASABE Standards (manure storage, land application equipment); Environment and Climate Change Canada / Canada–Ontario Lake Erie Action Plan.
Question text not reproduced: the examination questions are © Engineers and Geoscientists BC. Open the official past paper (linked at the top of this page) to read the question, then follow the worked solution below.
Part (a) — recipe.
Given. Table A.1 "Average" rows for the two feedstocks (attached appendix):
| Material | %N (dry wt.) | C:N ratio | Moisture (% wet wt.) |
|---|---|---|---|
| Broiler litter | 2.7 | 14 | 37 |
| Sawdust | 0.24 | 442 | 39 |
Find. The mass ratio of broiler litter : sawdust : water that gives a blended C:N of 30:1 and a moisture content of 60% (wet basis).
Approach. Convert each material's C:N and %N into an equivalent %Carbon (dry basis), blend the two solids on a DRY-MASS basis to hit the target C:N, then add water (which carries no carbon or nitrogen) until the wet-basis moisture of the whole mix reaches 60%.
| Quantity | Value |
|---|---|
| Dry-mass ratio, litter : sawdust | 2.29 : 1 |
| Recipe (wet basis, per 1000 kg litter) | 1000 kg litter : 451 kg sawdust : 812 kg water |
| Wet-mass ratio, litter : sawdust : water | 2.2 : 1 : 1.8 |
| Resulting C:N ratio (check) | 30.0 : 1 |
| Resulting moisture content (check) | 60.0% |
Part (b) — concerns with this mixture.
Several practical concerns arise from this recipe, beyond the arithmetic itself:
Data quality of the sawdust entry. Table A.1's "average" row for sawdust implies %C = 106%, a physical impossibility (Step 1 above), because the handbook's own note states these range/average values are pooled from different literature sources and "should not be considered as the true ranges or averages, just representative values" — the %N and C:N columns were not necessarily measured on the same samples. A prudent designer would seek a paired, internally-consistent data point (or a fresh lab test of the actual sawdust on hand) rather than trust the tabulated average outright; using a more typical wood %C of ~50% instead moves the recipe to roughly 1000 kg litter : 957 kg sawdust : 1078 kg water — a materially different sawdust and water quantity, though the qualitative conclusion (substantial bulking agent and a large water addition) is unchanged.
Water addition is a large fraction of the final mix (36% by mass). Hauling and uniformly incorporating >800 kg of water per tonne of litter is a real handling and equipment burden; in practice a composter would substitute some water with a wetter co-feedstock (e.g. liquid manure or leachate) where available, rather than adding clean water.
Broiler litter's own C:N is only an ESTIMATE. The table's footnote (a) flags the C:N value as "estimated from ash or volatile solids data" rather than measured directly, so the design C:N of 30:1 carries more uncertainty than the arithmetic alone suggests.
Bulk density / mixing behaviour. Sawdust (410 lb/yd³) is much less dense than broiler litter (864 lb/yd³); by volume the pile will look far more sawdust-dominated than the 2.2:1 wet-mass ratio suggests, which can mislead field crews mixing "by eye" rather than by weight.
Pathogen and ammonia loss risk before water is added. The intermediate 37.6% moisture blend (Step 3) sits below the ideal composting range (50–65%) and the fresh, N-rich litter is prone to ammonia volatilization if it sits un-composted at that stage — water should be blended in promptly rather than staged separately.