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Possible use of NIRS for the management of composting process

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Academic year: 2021

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(1)

L. Thuriès

1,2

, L. Bonnal

2

, F. Davrieux

2

, D. Bastianelli

2

1- Phalippou-Frayssinet S.A.,Organic Fertilisers, La Mothe, F81240 Rouairoux, France. [email protected]

2- CIRAD. Centre de Coopération Internationale en Recherche Agronomique pour le Développement, TA40/01, F34398 Montpellier cedex 05, France.

Composting agro-food wastes according to industrial processes can provide organic fertilisers with known (and constant) quality levels. For the industrial manufacturer, it is important to control the quality of a compost during its elaboration. A key of success is to respect the major composting stage: the thermophilic phase. The challenge is to complete this phase without wasting any supplementary week of composting.

The aim of this work was to explore the possibility of predicting by NIRS the composting degree.

When starting a new fabrication, the initial mixing of a 2000 tons pile can take several weeks (up to 12). Also, it is interesting to better know the composting age of a sub-pile.

The particular aim of this study was thus to estimate by NIRS the composting age as an important parameter of the composting degree.

The parameter measured was the compost age, CA, in days. When starting a new compost pile, CA=0, and the duration of the phase is 60 days on average.

Due to the heterogeneity of fresh materials, samples were dried (40°C) ground (<1mm sieve) before being scanned on a NIRS 6500 (Foss NIRSystems) in duplicate ring cups. Spectra acquired in reflectance were corrected with SNVD 2,5,5 (WIN-ISI) mathematical pre-treatment and calibrations were performed using a multiple linear regression (MLR, WIN-ISI).

The compost age (CA) varied widely (SD, Table 1), as the compost intermediates were included (CA from 0 to 103 d) coming from 6 series.

A series corresponds to a unique pile sampled regularly along the thermophilic phase. The model developed for CA was reasonably accurate, as the determination coefficient was close to 0.9; however, the RPD was under 3. The SECV was close to the corresponding SEC, indicating an acceptable robustness of the model.

Table 1: Performance of the general calibration model

These preliminary results show that it seems possible to assess the degree of composting, even if more efforts should be devoted to decrease the SECV to a more acceptable level (useful 4 d., ideal = 1 d.).

As ever seen for the general model, the population considered for the particular model had a high SD. The equation developed with 22 samples had a SEC reduced by about one third compared that of the general model. The R² overpassed 0.95, and the SECV was under seven days. Then the corresponding RPD was nettly above 3.

Introduction

Introduction

Results and discussion

Results and discussion

Materials and methods

Materials and methods

Conclusions and perspectives

Conclusions and perspectives

Fig 1. : Utilisation of NIR predictions during the management of the first stages of composts elaboration

Possible use of NIRS for the management

of composting process

CA = x days

Another calibration strategy was tempted. A particular MLR model was elaborated (Table 2) with a single series of 22 samples coming from an unique pile along the thermophilic phase.

Coffee cake Wool

waste

Mixing

Compost Age CA = 0 day

Composting Thermophilic phase complete? YES NO NIR predictions Turning Sheep manure 2.4 9.8 0.84 9.35 23.5 32.4 83 Compost age calibration statistics population n

parameter (in day) mean SD SEC SECV RPD

SD, Standard Deviation of parameter in the population SEC, Standard Error of Calibration

SECV, Standard Error of Cross-Validation RPD = SD / SECV

Composting

Table 2: Performance of the particular calibration model

4.7 6.96 0.97 6.04 32.6 50.4 22 Compost age calibration statistics population n

parameter (in day) mean SD SEC SECV RPD

SD, Standard Deviation of parameter in the population SEC, Standard Error of Calibration

SECV, Standard Error of Cross-Validation RPD = SD / SECV

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