Midterm Status Report 2002 and Application for Continuation in 2003

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1 Midterm Status Report 2002 and Application for Continuation in 2003 For research projects financed by grants from The Directorate for Food, Fisheries and Agro Business under the Danish Ministry of Food, Agriculture and Fisheries 1. Research program Research in organic farming (DARCOF II) 2. Project title and number CRUCIAL Closing the Rural Urban Nutrient Cycle (III.3) 3. Head of project Jakob Magid, Department of Agricultural Sciences - KVL 4. Participating institutes DJF DMU FSL *) KVL Danish Institute of Agricultural Sciences National Environmental Research Institute Danish Forest and Landscape Research Institute Royal Veterinary and Agricultural University 5. Other project staff KVL DMU FSL DJF-Foulum Simon Wrisberg, Lars Stoumann Jensen, Jacob Møller Paul Henning Krogh, Thomas Larsen Jacob Møller Bent T. Christensen, Gitte Rubæk 6. Project period (month, year) Start of project: August 2001 End of project: December 2004, but we recommend a no cost extension to allow the project to run until April 2006 *) FSL has transferred its composting facility and activities to KVL during 2002, and withdraws from the project as of 2003

2 7. Midterm description of the project, its results and progress, and application for continuation in 2003 A. Project summary (from application) Based on discussions with DARCOF it has been agreed to refocus the efforts in CRUCIAL. This is partly in lieu of the recently awarded EU-Life grant (Short-Circuit), that will allow further development of the composting facility into an On farm High temperature Low emission Low cost composting system that can be operated at farm level and at the same time comply with the upcoming EU regulation on the use of waste products in agriculture. This grant has been awarded on the basis of cofunding provided by the ongoing CRUCIAL project, why a readjustment of the CRUCIAL project in order allow a more comprehensive effort on composting practices for urban waste is appropriate. CRUCIAL Dissemination On-farm composting, Field trial, WP 1 and 2 ORWARE/DAISY WP3 Short-Circuit Fig1. The relationship between the Short-Circuit and CRUCIAL projects. Apart from a stronger focus on documentation of disease vector reduction, we propose to examine the potential of the composting process to reduce or eliminate GMOmaterials (a question raised by one reviewer), and to briefly examine claims made by American organic farming NGO s that the effluent from the composting process (compost tea) has phyto-sanitary and other plant health promoting capabilities. Furthermore we propose a restructuring of the field trial. According to Stig Milan Thamsborg, the single plots can be reduced in size without compromising a future use for studying disease transfer from urban fertilizers to grazing animals. Apart from a reduction in the size as well as the long-term cost of the experiment, a key benefit in this change is a reduction in the spatial variability of soil properties and harvestable yield (see discussion below). We also propose that sewage sludge and municipal waste compost are both added in normal rates as well as accelerated rates, in order to rapidly approach the ecotoxi-

3 cological soil quality limits for some heavy metals. This would allow within a reasonable timeframe the testing of the hypothesis that using urban fertilizers will not compromise key biological capabilities of the soil system as long as established ecotoxicological soil quality limits for heavy metals are respected. Finally it has been agreed to strengthen the modeling effort to include an extrapolation of the CRUCIAL results to more sandy soil and wetter climate found elsewhere in the country. Lars Stoumann Jensen, who is a key scientist in both the Biomod and Crucial project will be responsible for this. Table 1: Work package list with revised and original budgets WP no. Work package title participants Revised budget Original budget Start End Deliverable No: 1 Establishment and running of Longterm 2005/ field trials with urban fertilisers KVL a) Development of composting practises for food waste and human faeces FSL, KVL C and N dynamics of urban fertilisers KVL, DMU Agronomic research on P turnover in soil with applied Urban Fertilisers and DJF its subsequent availability in pot trials Soil quality monitoring programme DMU, KVL a) As in last years status report we request permission to extend the project life until April 2006, in order to be able to complete 4 growth cycles and initiate a 5 th cycle (see below, H). This is in agreement with the project document, and does not require any increase in the total budget. Table 2: Breakdown of budgets based on the specific objectives (see section B for further description of objectives) WP Objective Already spent Future allocation KVL FSL DMU DJF KVL FSL *) DMU DJF a b Total *) FSL has transferred its composting facility and activities to KVL during 2002, and therefore withdraws from the project as of Thus the FSL budget for 2003 should be reallocated to KVL, that has taken over FSL s responsibilities in the project

4 B. Objectives and expected achievements Objectives and their estimated man month allocation, (man month allocation from the original proposal given in brackets). WP s Objectives KVL FSL DMU DJF a 2 4b To provide the field-scale facility for assessing the feasibility of improved recycling of nutrients from urban areas to organic farms To facilitate the process of sustainable urban development, by inviting the public to visit the Long-term 12 (15) Trials 3 (3) To gain basic knowledge regarding co-composting of municipal solid waste and human faeces, with special emphasis on the effect of different mixing ratios and addition of green waste as structural material on self heating capacity, and nitrogen loss. 3 (3) To develop a High temperature Low emmision Low cost composting sys-tem that can be operated at farm level and at the same time comply with the upcoming EU regulation on the use of waste products in agriculture 6 (3) 3 (3) Examining the potential of the composting process to reduce or eliminate GMO-materials 8 (0) Examining claims that the effluent from the composting process has phyto-sanitary and other plant health promoting capabilities. 3 (0) To provide sufficient amounts of composted material for the field trials in a quality that will comply with future EU-standards on agricultural use of urban waste 4 (4) 3 (3) To perform a comprehensive mesocosm study on urban fertiliser impact on nutrient cycling where the temporal and spatial dynamics of plant nutrient cycling is linked to the biological activity of soil organisms 4 (6) To provide experimental data for modeling plant nutrient dynamics of soil receiving urban fertilisers via incubation studies and the mesocosm study mentioned 15 (15) above 8 (17) 2 (2) Model interpretation and extrapolation of urban fertilizers laboratory and field trial data 5 (3) To assess the availability of P in urban wastes and characterize the fertilizer value of waste-derived P following introduction to arable soil To deliver an initial characterisation of soil quality in the field experiment 3 (8) To initiate a long-term monitoring of soil biological quality in the field experiment 0 (4) 5 (11) Total number of months per institution (11)

5 C. Midterm results and progress C.1 Description (summary) of main results and conclusions A basic dataset on soil quality of the 11 hectare field has been generated Protocols have been developed for the individual urban fertiliser trials, including letters of agreements with parties that can deliver needed inputs. A field-scale facility for assessing the feasibility of improved recycling of nutrients from urban areas has been developed. The design of the field trial was discussed at length in a recent workshop (september 2002) involving stakeholders from DARCOF as well as scientists representing human and animal health interests from KVL. The field design has been further discussed with the director of DARCOF. Some changes to the preliminary design will be made as a result of this discussion. A protocol for composting household waste together with human faeces sludge has been developed. Laboratory studies on composting of human faeces have been initiated. A 30 m 3 facility for co-composting of municipal solid waste and human faeces is currently being developed. This activity has been strengthened by a grant from the EULIFE-ENVIRONMENT programme (see Annex 1), that will allow further development of the composting facility into a High temperature Low emission Low cost composting system that can be operated at farm level and at the same time comply with the upcoming EU regulation on the use of waste products in agriculture A national workshop on Composting Plant Residues and Human Waste in support of High Value Organic Plant Production was organised by the CRUCIAL project on 28 th February at KVL A long-term monitoring of soil biological quality in the field experiment has been initiated Details of the common KVL/DMU mesocosm study on soil food webs and urban fertilisers have been planned and the experimental work has been initiated

6 C.2 Fulfilment of tasks and deadlines in individual work packages WP1 Establishment and running of Long-term field trials with urban fertilisers Time schedule Deviations, if any* Deliverables Annual reports Materials and protocol for guided tour (public relations) May 2002 Report on crop yields and quality, and soil N min status over (input needed in WP3) Dec 2004 Milestones Establishment of permanent grass strips Oct March 2002 Spreading of fertiliser with high N availability (to be repeated yearly) Apr Sowing of crops (to be repeated yearly) Apr Characterization of crop growth (to be repeated yearly) May - August Public presentation of the field experiment ((to be repeated yearly, and on request) Jun Spreading of fertilisers with low N availability (to be repeated yearly) Nov WP2 Development of composting practises for food waste Time schedule according and human faeces to application Deliverables Composted MSW and faeces for use in the field experiment each year from autumn/winter 2002 Oct 2002 & onwards Report on best practice for full-scale co-composting of Dec 2003 municipal solid waste and human faeces based on laboratory scale experiments and trials with meso-scale experiments on KVL s experimental station Presentation at conference 2004 Scientific manuscript on composting trials Jul 2004 Report on phyto-sanitary effects of compost effluent Jul 2005 Scientific manuscript on GMO materials in compost Jul 2005 Establishment of a composting facility at KVL s experimental station Milestones Deviations, if any* Dec 2002 & onwards Apr Sep 2002 First meso-scale composting trial completed (to be repeated Oct Dec 2002 each year) Laboratory studies on composting completed July 2004 Laboratory studies on GMO material in compost completed Dec Trials with compost effluent completed Dec. 2004

7 WP3 C and N dynamics of urban fertilisers Deliverables Contributions to status and final project reports Time schedule according to application Oct 2002 & onwards Deviations, if any* Synthesis report comprising the mesocosm system elements Dec 2003 Popular presentation 2004 Four scientific papers Milestones Comprehensive mesocosm study completed Dec Further incubation studies on quality and temperature effects on temporal patterns of nutrient fluxes completed July 2004 Model interpretation of relevant parts of the aforementioned milestones Dec Simulation completed of the field trials based on parameterisation of urban fertilisers, climate data and relevant July 2004 crop modules and concomitant testing of the predictive capability based on data from the field (WP1) Work Package 4 has yet to be initiated due to the 1 year delay of the project funding WP5 Soil quality monitoring programme Deliverables Contributions to status and final project reports Time schedule according to application Oct 2002 & onwards Deviations, if any* Report on soil characteristics, and motivated recommendation Dec 2002 Oct 2002 for the lay-out of the field trials (enclosed) Report on urban fertiliser impact on soil quality 2004 Milestones Establishment of soil archive Sep Layout of plots Oct March 2002 revised Dec Sampling of plots for faunal and other biological characterisation Oct (soil quality baseline study) Completed baseline study Mar Sampling of plots for faunal and other biological characterisation Aug Completed soil quality impact study after 3 years of treatment/fertilisation Oct D. Description of deviations and subsequent adjustments of plans Based on discussions with DARCOF it has been agreed to refocus the efforts in CRUCIAL. This is partly in lieu of the recently awarded EU-Life grant, that will allow further development of the composting facility into a High temperature Low emission Low cost composting system that can be operated at farm level and at the same time comply with the upcoming EU regulation on the use of waste products in agriculture. This grant has been awarded on the basis of the co-funding provided by the on-

8 going CRUCIAL project, why a readjustment of the CRUCIAL project in order allow a more comprehensive effort on composting practices for urban waste is appropriate. Apart from more focus on documentation of disease vector reduction, we propose to examine the potential of the composting process to reduce or eliminate GMO-materials (a question raised by one reviewer), and to examine claims made by American organic farming NGO s that the effluent from the composting process (compost tea) has phytosanitary and other plant health promoting capabilities. GMO s in urban waste (WP2 objective 4a) Organic farmers and consumers are concerned about risks of contamination of their crops with genetically modified organisms. One such risk factor could be the use of compost containing viable seeds or other viable structures from genetically modified plants. Another danger could be the propagation of bacterial GMO into the environment from bacteria surviving the composting process. We have searched the literature and have found no publications in refereed journals on these subjects. Fundamental research into this area is therefore warranted. If the composting process is well controlled with sufficient oxygen to promote extensive decomposition of the material and high temperature is reached, the number of seeds of any kind that survives will be very limited. Indeed the likelihood of finding any viable plant material in the compost will also be very low. However, some concern about the survival and propagation of genetically modified DNA is warranted. Questions that come into mind are: 1) Can GMO DNA persist during the composting process? 2) Can naked GMO DNA be taken up by bacteria in the compost? 3) Can these bacteria survive during composting 4) Can GMO DNA spread to indigenous organisms (bacteria/plants) in soil fertilized with the compost? That DNA may persist during composting is highly likely, since the temperature that has to be reached in the compost according to the EU regulative is 70 C which is not a temperature that on its own will break down DNA. As a comparison the elongation temperature during PCR is 72 C. DNA may become single stranded but it will not be broken down. As a matter of fact, single stranded DNA is more easily be taken up by the naturally competent (able to take up DNA) bacteria that take up naked DNA from the environment. The DNA may be either utilized or incorporated into the bacterial chromosome or plasmids harbored in the bacteria. Most of the naturally competent bacteria belong to the Genus Bacillus which are Gram-positive spore forming bacteria, and thus very heat resistant. The spores may endure in the soil or compost for years until the right germination conditions are present. There have been many studies that show horizontal gene transfer between different species of soil bacteria and even transfer between pro- and Eukaryotes has been reported. This means that the possibility of transfer of GMO DNA to indigenous species cannot be excluded. We will undertake an elucidation of the first 3 questions raised above under controlled laboratory experiments. If time is sufficient we will also pursue the 4 th issue under laboratory conditions. Phytosanitising effect of composting effluent (WP2 objective 4b) There is a growing interest - especially in the United States - regarding the use of compost "tea" in organic agriculture as an alternative to pesticides and as a nutritional supplement. Compost tea is made from mature compost by steeping the compost in water and subsequently filter the solution to prevent clogging of irrigation lines etc. used for applying it to the crop. Thus, compost tea contains water-soluble nutri-

9 ents as well as microorganisms originating in the compost. The phyto-sanitary effect supposedly results from the presence of beneficial microorganisms in the compost tea that out-competes plant pathogens found on the crop. The HILO-compost system under development will supply high quality compost that complies with EU as well as Danish regulation regarding the hygienic quality of the product. Compost tea made from this compost will first be tested for its phyto-sanitary effects in a model laboratory system. The experiments will focus on quantifying the phyto-sanitary effects - if any - of applying compost tea to the leaves of the plants or direct effects on pathogenic organisms. If an effect is found, further tests will be setup to pinpoint the active substances. The field trial (WP1): Approaching the limits It has proven to be very important to justify the establishing of historical sites through long-term field experiments, since most non-soil scientist have difficulties in grasping the needs for this. The CRUCIAL field trial will provide data on the soil nutrient cycling as affected by different urban and reference fertilizers that will be used for validating model calibrations based on the laboratory studies. However the implications of the longer-term utility of the field trial are all important for the possibilities for closing the rural-urban nutrient cycle in the future. This has been stressed in the original application in sections describing the needs to avoid compromising the production systems. However we will briefly reiterate this line of arguments in the following. It is well established that certain key functions of soil biology can be completely destroyed or profoundly disturbed by the use of heavy metal polluted sewage sludge. Thus both German and British long-term field trials have shown that populations of rhizobia were rendered incapable of fixing atmospheric nitrogen in their symbiosis with white clover at moderately low soil metal concentrations (Giller et al., 1998). Furthermore it has been shown that infection from both native and inoculated VAMspores was strongly delayed in these soils (Koomen et al., 1990) thus hampering the beneficial symbiosis for nutrient and water uptake that support many plants growing under sub-optimal conditions. It is clear, that as research continues, the minimum loadings at which negative effects are observed are likely to become smaller and smaller (see for example Dahlin et al., 1997), so that decisions on soil protection will inevitably have to be made on the basis of what is deemed to be an acceptable'' risk of damage to microorganisms and microbial processes in soil. This knowledge has been taken into account in the recently established guidelines for ecotoxicological soil quality limits for heavy metals, so for all that we know approaching these limits should not compromise key soil biological functions. However it is clear that substantial and discernible effects are likely to be measurable at these concentrations (Fig.2). Apart from heavy metals, urban fertilizers will inevitably contain xenobics, e.g. medicinal substances, detergents and hormone-like substances and as we have recently documented human urine from urban ecological demonstration projects contained quite substantial amounts of estron (18-61 nmol L -1, Wrisberg et al, 2001). A preliminary risk assessment indicated that this would not be likely to result in toxic effects on terrestrial plants, due to the adsorption and subsequent decomposition of estron in the soil matrix.

10 Fig. 2. Effect of addition of heavy metals on base respiration in different soils in laboratory ecotoxicological studies. Open symbols indicate the highest amount of metal added that did not produce an effect (HNOED), closed symbols represent the lowest amount added that resulted in a decrease in the rate of base respiration (LOAED). Arrows indicate the current Danish ecotoxicological soil quality criteria for Cu and Zn. (Adapted from Giller et al. 1998). Since the urban fertilizers are likely to contain almost as many different xenobiotic compounds as can be found in the Merck index, it is entirely justified to worry about unforeseen ill effects of such substances in the ecosystem, but it will never be possible or even meaningful to assess these risks using a single compound approach. Therefore we maintain that the most efficient way to ascertain a safe use of urban fertilizers in the future is through the establishment of historical sites, where specific urban fertilizers have been used systematically over a number of years. We therefore propose that sewage sludge and municipal waste compost are both added in normal rates as well as accelerated rates, in order to rapidly approach the ecotoxicological soil quality limits for some heavy metals. This would allow within a reasonable timeframe (see Table 3) the testing of the hypothesis that using urban fertilizers will not compromise key biological capabilities of the soil system as long as established ecotoxicological soil quality limits for heavy metals are respected. The accelerated loading approach was suggested to the background panel including representatives from the organic farming association, that came up with the original recommendations of establishing the field trial. At this point it was not favored because it implies an overuse of nutrients. However, in the light of the pressures to produce results within a short period we recommend this approach once more.

11 Table 3. Years to reach the critical ecotoxicological heavy metal concentration in the Crucial experiment, based on the calculation method described by Magid (1998). Standard values for heavy metal content have been taken from Eilersen et al. (1998) and Wriesberg et al. (2001). Municipal Solid waste compost Municipal SW compost accelerated (factor 3) 'Normal' sludge Worst case sludge 1 accelerated (factor 3) Zn Cu Sewage sludge containing maximum permissible heavy metal content according to current Danish regulation In summary we do not anticipate substantial negative effects on key soil biological functions during the first 5 years of the trial. However, as stated above, the trials will be of immediate use for validating model calibrations obtained on the basis of the laboratory studies, and this is a necessary quality assessment before the attempts to extrapolate to other soil types and climatic conditions. Spatial variability of response variables in the field experiment During the first year of the field trials the yields of spring wheat varied from t ha -1 depending on fertilization regime (Table 4). Table 4. Preliminary results from harvested grain yield (kg dry matter ha -1 ) from spring wheat (2002) having received appr. 100 kg total N. (N-content in degassed household waste and sewage sludge has yet to be confirmed). Superscript letters indicate statistically different yields on plots with intermediate and higher organic matter content. Soil Organic C Deep Litter Control (unfertilised) Green Manure Sewage sludge MSW compost MSD 1) % 1846 c 2621 b 2792 b 3428 a n.a. 481 Green Manure Cattle Slurry Human Urine NPK Degassed HHW % 3254 b 3694 ab 3875 ab 3940 ab 4411 ab 797 1) Minimum significant difference (p < 0.05) using Tukeys test for multiple comparison of means According to Stig Milan Thamsborg, the single plots can be reduced in size without compromising a future use for studying disease transfer from urban fertilizers to grazing animals. This allows a reduction in the size as well as the long-term cost of the experiment, and also a reduction in the spatial variability of key soil properties. In the current setup the plots are distributed over an organic matter gradient of % soil carbon and a sand content gradient of appr %. This could be reduced to a gradient of % soil carbon and sand content gradient of appr %, by reducing the size of the plots to approximately. 50% of their current size (Figure 3). The statistical analysis of yield data (Table 4) indicates that there is less spatial variability is between the plots with intermediate soil carbon content. Thus it is likely that relocating all treatments to this part of the land will reduce spatial variability of other biological responses to the treatment effects.

12 Figure 3. Revised layout of field experiment

13 Figure 4. The relocated field-trial.

14 It is commonly observed that the toxicity (i.e. bioavailability) of heavy metals is closely linked to soil organic matter content, because a higher organic matter content will both protect microorganisms in micro-sites and act as an adsorbent for the heavy metals. Furthermore a larger content of non-humified organic matter will act as a source of energy for the decomposing system, and contribute to a decrease in the toxic effects of heavy metals (Giller et al., 1998). The spatial variability of the impacts of xenobiotics found in urban waste is not well known (Müller and Magid, 1998). However dramatic effects as those described above will be easily detected. Since we are at this point not certain which ill effects there might be (and hopeful that there will be none at the levels of loading that are applied) it is next to impossible to predict detection limits. However it is likely that they would vary with organic matter content and texture. We therefore believe it would be pertinent to include an accelerated loading treatment with deep litter or cattle dung, in order to attain similar loadings with organic matter believed to be harmless, and already accepted in organic farming practices. Anticipated outcome of the CRUCIAL field trial. Year # Hypothesis / Outcome Well prepared and matured MSW compost will produce a more predictable and higher MFE value than similar animal manures (deep litter) 2 MFE value of human urine can be at least as high as easily available animal manures (cattle slurry or urine) 3 Sewage Sludge N eff > 35% of Mineral N MFE value of sewage sludge can be improved by spring application 4 Catch crops and green manures are necessary in crop rotations with urban fertilizers if improved MFE values are to be achieved Key soil biological functions not impaired by accelerated 'worst case' sewage sludge (ecotoxicological limits for heavy metals approached) 6 Phyto-sanitary effects on soil treated with MSW compost measurable Establishment of long-term residual effects of MSW compost and Sewage Sludge on soil N supplying capacity 8 Soil Organic Matter levels measurably increased in MSW compost and Sewage Sludge treated plots (use for model validation) Key soil biological functions not impaired by accelerated MSW compost (ecotoxicological limits for heavy metals approached after ca. 10 years) 10 Key soil biological functions not impaired by accelerated 'worst case' sewage sludge (ecotoxicological limits for heavy metals exceeded by year 5-6) Notes on the impact of spatial variability: Hypothesis 1-4 require minimum significant differences in dry matter yields treatments and the unfertilized control at the p<0.05 level. This degree of resolution has already been obtained during the first year of the trial (table 4), and will tend to accumulate with time, and with the proposed changes in the plot-layout, that will further reduce the impact of spatial variability. Hypothesis 5-7, 9 and10 will involve laboratory testing. Previously published studies have shown dramatic reductions in symbiotic relationships for VA-mychorhiza and rhizobia (factor ), why spatial variability is not expected to give rise to problems in testing these effects (that we do not expect to occur). Other measures, such as susceptibility to diseases and vitality of higher trophic levels in the soil foodweb are expected to respond less dramatically, and will thus be more susceptible to spatial variability. However, we are presently able to measure increased disease resistance under greenhouse conditions already after one single compost addition to cucumber plants grown in peat (Hanne Carlsen, Master thesis under publication).

15 Ad.1. To date, the number of systematic studies of MSW compost as a source of plant nutrients have been limited. In a review, Müller and Magid (1998) noted that of 38 different composts from German municipal treatment plants, more than half showed net immobilization of N, during the first 12 weeks after use. These effects are most probably due to the preparation of the compost (degree of maturity, loss of N during composting, which materials were used as structural components to ensure aeration during composting). We hypothesize that it will be possible to produce compost from Municipal Sorted Waste, that will have a predictable total fertilization potential of 30% of total N, compared to that of mineral fertilizer N, during the first year of treatment. Ad.2. Müller and Magid (1998) collected data from field and pot trials compiled from Sweden, on the use of human urine. Very few solid data are available, indicating that NH 3 volatilization may account for 10% losses of N during the first 24 hours after distribution to the field. Fertilization efficiency is expected to be 70-85% of total N, compared to that of mineral fertilizer N, during the first year of treatment Ad. 3. In Danish field trials with winter wheat, it has been found that the fertilization efficiency was 25% of total N in sewage sludge, compared to that of mineral fertilizer N, during the first year of treatment (Müller and Magid, 1998). However in these trials the fertilization was done during autumn. We anticipate that it will be possible to increase the efficiency of N from sewage sludge treatments to app. 35% of mineral N by a different timing (spring sown crops) and use of cover crops to minimize losses from the system. Ad. 4. In the original proposal we stressed the need for using green manures and catch crops in order to successfully utilize urban fertilizers with a low content of readily available N. Ad. 5. Subjected to tests on biological nitrogen fixation capacity and VA-mychorhizal infection, the soil from the accelerated worst case sewage sludge treatment is not expected to be negatively affected compared to a relevant control treatment having received similar loadings of organic matter from manure/deep litter treatments. Ad. 6. A number of publications have indicated that MSW compost will have a longterm phyto-sanitary effect on soil-borne pathogens (Müller and Magid, 1998). This should be testable after 5-8 years of continuous use on the same plots. Ad 7-8. The long-term effects of MSW compost and sewage sludge are poorly established. We recently estimated that after 50 years of use 20% of the added carbon from MSW compost would be sequestered in soil, however the data used in this estimate was derived from laboratory studies. Little is actually known about the longer term effects of these products on the base mineralization rate of C and N. After 8-10 years of continuous use, these can be established. Ad Subjected to tests on biological nitrogen fixation capacity and VAmychorhizal infection, the soil from the accelerated worst case sewage sludge and accelerated MSW compost treatments are not expected to be negatively affected compared to a relevant control treatment having received similar loadings of organic matter from manure/deep litter treatments. If confirmed this will give a strong indication about the sustainability of long-term usage of these urban fertilizers at normal rates, with regard to the agro-ecosystem integrity.

16 Model interpretation and extrapolation of urban fertilizers laboratory and field trial data (WP3 objective 8) Based on the discussion with DARCOF it has been decided to extend and clarify objective 8 (WP3). The objective is to utilize existing, well-tested simulation models (Daisy and/or FASSET) for interpretation of the urban fertilizers field trial data. Through the DARCOF funded BIOMOD project the Daisy and FASSET simulation models have been extensively re-structured, recalibrated and further developed on a large number of field trial datasets from a variety of soil types, climates, crop rotations etc. This facilitates the extrapolation of the urban fertilizers field trial data to other farming situations than that of the experiment. The only additional requirement is to parameterize selected urban fertilizers for the models on the basis of the mesocosm and lab. incubation experiments of the project. The integration with the BIOMOD project is ensured through the participation of Lars Stoumann Jensen in both projects. Literature cited in section D Dahlin S., Witter E., Mårtensson A. M., Turner A. and Baath E. (1997) Where's the limit? Changes in the microbiological properties of agricultural soils at low levels of metal contamination Soil Biology and Biochemistry 29, Eilersen A.M., Magid J., and Tjell J.C. (1998) Genanvendelse af affald på jord. Chapter 5.6, In Affaldsteknologi. Ed. T.H. Christensen, Teknisk Forlag, København, Giller K.E., Witter E., and McGrath S.P. (1998) Toxicity of heavy metals to microorganisms and microbial processes in agricultural soils: a review. Soil Biology and Biochemistry, 30, Koomen, I., McGrath, S.P. and Giller K.E. (1990) Mycorrhizal infection is delayed in soils contaminated with heavy metals from past sewage sludge applications. Soil Biology and Biochemistry 22, Magid J. (1998) Forurening af landbrugsjord med tungmetaller med særlig fokus på kobber og zink. ATV Møde Diffuse forureninger på landbrugs- og byjord. Schæffergården , s Müller T. and Magid J. (1998): Jordbrugets anvendelse af byaffald i Nord og Central Europa. In: Magid J. (Ed.): Recirculering fra by til land? Om næringsstoffer på afveje... Dep. of Agricultural Sciences, The Royal Veterinary and Agricultural University, Copenhagen Wrisberg S.; Eilersen A. M., Nielsen S.B., Clemmesen K., Henze M. og Magid J. (2001) Vurdering af muligheder og begrænsninger for recirkulering af næringsstoffer fra husholdninger fra by til land.miljøprojekt/ Aktionsplanen for økologisk omstilling og spildevandsrensning. Miljøstyrelsen. E. Project publications 1. Articles in international, scientific journals with review procedures Færge, J., Magid, J. and de Vries, F. P. (2001) Urban Nutrient Balance Modelling

17 for Bangkok. Ecological Modelling, 139, Presentations at congresses, symposiums etc. Within the auspices of the Nordic Agricultural Research Forum a workshop was organised by the CRUCIAL project on 20 th - 21 st of August 2001 on URBAN AREAS - RURAL AREAS AND RECYCLING THE ORGANIC WAY FORWARD? A DARCOF proceedings will be published based on 15 contributions from Scandinavian and international researchers in the field A national workshop on Composting Plant Residues and Human Waste in support of High Value Organic Plant Production was organised by the CRUCIAL project on 28 th February 2002 at KVL. Magid J. (2002) Byernes affaldshåndtering og næringsstofkredsløb. Chapter 10. In: Visioner for Fremtidens Jordbrug. Eds. E.S. Jensen, H. Vejre, S. Højbjerg Bügel and J. Emanuelsson, Gads Forlag, København, Magid J., Granstedt A., Dýrmundsson Ó., Kahiluoto H., Ruissen T., (2002) Urban areas Rural areas, and recycling the organic way forward?. Darcof report no. 3, pp. 190 The following papers may be downloaded from: Magid J. (2002) Hard and soft science issues to be negotiated to improve urban metabolism. In Urban areas Rural areas, and recycling the organic way forward?. Eds. Jakob Magid, A. Granstedt, Ó Dýrmundsson, H Kahiluoto, T Ruissen, Darcof report no. 3, 12 pages, In press Reeh and Møller (2002) Evaluation of bifferent biological waste treatment strategies. In Urban areas Rural areas, and recycling the organic way forward?. Eds. Jakob Magid, A. Granstedt, Ó Dýrmundsson, H Kahiluoto, T Ruissen, Darcof report no. 3, 10 pages, In press 3. Articles in agricultural journals etc. A National Daily Newspaper (Berlingske): Andersen Pauli: Forskere ser en guldgrube i de danske kloakker. Berlingske fredag d. 5 oktober 2001 From the Danish Center for Urban Ecology: Wrisberg Simon, Eilersen Ann Marie: Nye håndteringssystemer til recirkulering af spildevand og organisk affald fra byer. Foreningen Dansk Byøkologi juni nr.2 årgang 4. From the Danish Public Service Radio (Program 1) The Miljømagasinet 19 th april 2002, running title Urin kan blive fremtidens gødning ( Urine may become a future fertiliser ), please refer to: URL:

18 4. Oral presentations at meetings, field days etc. Presentations for 2 high-school groups on separate occasions in September 2001, Jakob Magid, KVL Presentations for 3 high-school groups on separate occasions in february- april 2002, Jakob Magid, KVL Presentations for 4 high-school groups on separate occasions in november- December 2002, Jakob Magid, KVL Association of Organic Farmers theme lectures 7 th November 2001 Nutrients in circulation how can urban fertilisers contribute, Jakob Magid, KVL F. Scientific education (ph.d. and post doc.), including visiting scientists and visits abroad A European Science Foundation LinkEcol grant supported visting scientist, Dr Michaël Coeurdassier. He has conducted a study to evaluate the quantitative effects of decreasing the diversity, using pesticides as a tool, on the foodweb structure of the soil communities (particularly microarthropods, earthworms and bacteria) and the possible consequences of community structure modifications on soil functions, i.e. decomposition of cow dung and N cycling. G. National and international co-operation Participation in ORIO a Nordic training and educational network on eco-sanitation development, headed by Petter Jenssen, NLH, ÅS, Norway ( ) The CRUCIAL project is part of a portfolio hosted by: NUTRAP CENTRE FOR APPROPRIATE TECHNOLOGIES FOR NUTRIENT RECYCLING FROM HUMAN WASTE TO AGRICULTURE IN PERI-URBAN AREAS A number of research departments have signed the MOU and take part in its activities. For further information on NUTRAP please refer to: H. Critical reflection on the project The final decision to initiate the project was delayed in the Ministry of Agriculture, and the letter of grant was only released in the end of April Therefore there was a full year delay in the commencement of the project that has been running since 1 st August Thus at this point in time we have been working for only about 1 year. Recommendations for a project life extension Given that the project is intended to initiate a long-term experiment (WP1) and a biological soil quality monitoring programme (WP5), we wish to be granted permission to extend the project life to April 2006, in line with the intention of the original application, that allowed the completion of 4 growth cycles, and the initiation of a 5 th cycle. The current funding is sufficient for this, and therefore we would ask for a no cost

19 extension. The ministry has recently indicated that the project should be completed by 2005, but we recommend a slightly longer project completion period, in line with the intention of the original project proposal. Major changes in the project and project context The project has by and large been running according to its revised schedule (1 year delayed due to funding issues), but some external events have had an impact on its implementation. At the end of 2001 the project leader became critically ill, and has been treated during 2002 with bone-marrow transplantation. This has apparently been successful, but necessitated some month s leave of absence and caused a delay in the implementation of WP3. The new governments priorities and cut backs on the environmental sector necessitated some institutional changes in beginning of Therefore the Danish Forest and Landscape Research Institute decided that the composting technology focus should be dropped from their program, and have decided to transfer the composting laboratory as well as the existing project portfolio to KVL. This institutional change has caused some months delay in WP2, but we anticipate that WP2 will be completed successfully. While working on composting we have noted that the Indore method is not a mesophilic approach, as it was originally described. Furthermore, the recent food safety crisis in Europe has resulted in a stricter regulation on agricultural use of organic waste containing material of animal origin, e.g. organic household waste, requiring a hygienisation (>70 C for 1 hour) before use. Therefore we have refocused the R&D effort in WP2 in order to be able to comply with future EU standards. The EU has recently committed a substantial financial support for our R&D effort through the LIFE instrument, which we believe will allow us to further develop the farm based High Temperature Low Emission Low Cost composting system to be used in WP2. A short description of the LIFE-project is enclosed (Annex 1). We would like to further strengthen WP3 with a PhD student (joint between DMU and KVL) from the SOAR school.

20 8. Budget A. Account for any change in budgets We seek permission to extend the project life into 2006, given that the initiation of the project is a year delayed, and that the project is a long-term venture. We have currently permission to extend the project until This change in the budget is in line with the intention of the original application, that allowed the completion of 4 growth cycles, and the initiation of a 5 th cycle.

21 B. Budget for the whole project (1.000 DKr) Total consumption of funds from DARCOF and expected consumption this year and coming years Total Man-months 0,5 0,3 0,5 1,0 1,0 1,5 5 Scientific personnel 2,3 15,5 14,3 21,2 13,9 0,0 67 Technical personnel 0,0 5,1 6,9 7,0 2,9 1,2 23 All institutions Total Salaries Salary (coordination) Scientific personnel Technical personnel Other operational costs Transport af 'By-gødninger' Special field operations Composting facility and equipment Characterisation of the experimental field Direct costs Indirect costs (20% of direct costs) Total Comments: Due to the changes in government policies the Danish Forestry and Landscape Research Institute have decided to transfer their composting laboratory and project portfolio to KVL. Therefore FSL s budget for 2003 should be incorporated into KVL s budget.

22 9. Signatures and stamps Name Institute Date Signature Head of project

23 Appendix I. Fyldigt dansk sammendrag af forskningsprojektet og dets resultater Projektnummer og titel III.3 Recirkulering af næringsstoffer fra by til land - Etablering af fastliggende forsøg med bygødninger samt tilhørende agronomisk forskning og forskning i jordkvalitet (CRUCIAL) Delprojekter Nr. Titel Ansvarlig Budget (1.000 kr.) Start Slut 1 Etablering og drift af fastliggende forsøg med by-gødninger 2 Udvikling af komposteringspraksis for husholdningsaffald og human fæces 3 Kulstof og kvælstof dynamik ved anvendelse af bygødninger 4 P omsætning i jord tilført bygødninger og efterfølgende tilgængelighed i karforsøg Jakob Magid Jakob Møller Jakob Magid Bent Christensen 5 Monitering af jordkvalitet Poul Henning Krogh / 2006 a) / / 2006 a) 323 a) Der anmodes ligesom ved sidste års afrapportering om forlængelse af projektperioden til og med April 2006, for at kunne gennemføre 4 dyrkningssæsoner og påbegynde en 5 te (se nedenfor). Dette er i overensstemmelse med den oprindelige ansøgning, og vil ikke kræve nogen samlet udvidelse af projektets budget. Sammendrag Byerne er i praksis afspaltet fra landområderne hvad angår recirkulering af næringsstoffer og organisk stof. Dette forskningsprojekt er en del af en sammenhængende indsats for at genetablere kredsløbet mellem land og by og videreudvikle affaldshåndteringen i byerne, så der kan leveres brugbare gødningsstoffer til økologisk jordbrug. Gennem etablering af fastliggende forsøg med bygødninger vil det blive muligt at vurdere mulighederne for forbedret recirkulering fra byområder til økologiske bedrifter. Med sit fokus på komposteringsmetoder, forskellige bygødningers omsætning i jord og tilgængelighed for planter vil det frembringe praktisk anvendelige resultater. Med etableringen af et moniteringsprogram for biologisk jordkvalitet søger det at tage bestik af evt. uforudsete negative virkninger af øget recirkulering. Endvidere vil det understøtte fremtidige forskningsaktiviteter vedr. sundhed og fødevaresikkerhed. Endelig vil projektet etablere en platform for offentlig debat om recirkulering fra by til land. På grundlag af det første års erfaringer, anbefales det at arealet der anvendes til

24 markforsøget reduceres. Dette vil kunne mindske den forventede variabilitet i bl.a. udbytte respons, og i andre parametre der er væsentlige for at vurdere bygødningers evt. utilsigtede virkninger på agro-økosystemet. På baggrund af en medfinansiering af EU midler (EU-Life programmet) kan der lægges mere vægt på at belyse effekter af kompostering, herunder smitstofreduktion, overlevelse af GMO materiale og plante-beskyttende virkninger af kompostekstrakter. Projektet er inddelt i fem delprojekter: 1. Etablering og drift af fastliggende forsøg med by-gødninger I delprojektet er der etableret et feltlaboratorium for anvendelse af bygødninger. Herved kan det biofysiske grundlag for forbedret recirkulering fra by til land undersøges, både hvad angår gødningernes virkning, og de evt. miljø- og sundhedsmæssige risici der er forbundet med dette. Der er etableret 39 store) parceller som er adskilt af permanente græs striber, for at hindre udveksling af jord (og evt. smitstoffer og fremmedstoffer) mellem parcellerne. Et andet vigtigt mål med delprojektet er at fremme bæredygtig byudvikling, ved at invitere offentligheden (journalister, skoleklasser, m.v.) til at besøge feltlaboratoriet. Der er udviklet informationsmaterialer og plancher til brug ved "guided tours", og der er stor interesse for at høre om aktiviterne og problem feltet blandt besøgende gymnaiseklasser. 2. Udvikling af komposteringspraksis for husholdningsaffald og human fæces Der tilvejebringes grundlæggende viden vedrørende samkompostering af organisk husholdningsaffald og human fæces. Der vil blive lagt særlig vægt på effekten af forskellige blandingsforhold og tilførsel af strukturmateriale på varmeudviklingen, kvælstof tab og iltforbrug. Med tilskud fra EU er der sikret en styrkelse af denne indsats, med henblik på at udvikle en gårdkomposteringsteknologi (High temperature Low emission low cost) der kan sikre at det komposterede byaffald opnår en kvalitet der er i overensstemmelser med det fremtidige EU direktiv vedr. jordbrugsmæssig anvendelse af affald. Dette kræver at der under komposteringen opnås temperaturer på over 70 C. Der vil yderligere blive set på spørgsmål vedr. overlevelse af GMO materiale og plantebeskyttende virkninger af kompostekstrakter. 3. Kulstof og kvælstof dynamik ved anvendelse af bygødninger Målet med delprojektet er at gennemføre omfattende studier af bygødningers omsætning hvor den tidslige og rumlige dynamik af næringsstofkredsløbet knyttes til den biologiske aktivitet af mikroorganismer og jordboende dyr. Desuden skal projektet tilvejebringe eksperimentelt grundlag for at modellere kvælstof omsætningen i jord der tildeles bygødning. Endeligt skal udvalgte bygødninger parameteriseres til DAISY modelsystemet, og modellens forklaringskraft skal afprøves ved at undersøge dens evne til at simulere detaljerede målinger fra feltstudiet. Derved kan den indsamlede viden om bygødninger tolkes mere generelt, med henblik på anvendelse under andre klimaforhold, afgrøder og jordtyper. 4. P omsætning i jord tilført bygødninger og efterfølgende tilgængelighed i karforsøg De relevante bygødninger karakteriseres m.h.t. P fraktioner og deres omsætning i jord følges gennem inkubationsstudier. Bygødningerne anvendes i karforsøg på udvalgte jordtyper med forskellig P-status, som tilsås med græs. Planteoptagelsen af P

25 følges, samtidig med ændringer i jordenes P fraktioner. 5. Monitering af jordkvalitet Der er lavet en grundig karakterisering af forsøgsarealerne ved igangsættelsen af forsøget. Der vil blive opbygget et jordarkiv med udgangspunkt i 300 målepunkter i 2 dybder, som kan bruges ved senere undersøgelser af evt. fremmedstoffer og tungmetaller. Karakteriseringen har bidraget til den fysiske udformning af markforsøget, og den præcise udformning af moniteringsprogrammet, som er etableret med henblik på tilbagevendende at følge ændringer i den biologiske jordkvalitet, efterhånden som de anvendte gødningstyper præger jordens kvalitet og frugtbarhed. Det er dog besluttet at der ikke foretages yderligere monitering indenfor projektperioden. Status 2002 Beslutningen om igangsættelse af projektet blev udsat i Direktoratet for Fødevare Erhverv og bevillingsskrivelsen først afsendt i slutningen af April Derfor er projektet 1 år forsinket, og har kun været i gang siden August Således har vi i skrivende stund været i gang i ca. 1½ år. Projektet har i det store hele udfoldet sig planmæssigt, men visse udefra kommende forhold har haft betydning for dets implementering. Ved udgangen af 2001 blev projektlederen alvorligt syg, og er i løbet 2002 blevet behandlet med knoglemarvstransplantation. Denne er gået godt, men har nødvendiggjort nogle måneders sygefravær, og ført til en forsinkelse i implementeringen af WP3. Som følge af den nye regerings prioriteringer på miljøområdet har Forskningscenter for Skov og Landskab besluttet at nedlægge komposteringsområdet. FSL har anmodet KVL om at overtage kompostlaboratoriet og den medfølgende projektportefølje, og KVL har fundet en mulighed for at ansætte den relevante ekpertise på området. De seneste fødevaresikkerhedsproblemer i Europa har resulteret i en stramning af reguleringen af jordbrugsmæssig anvendelse af affaldsprodukter, som kræver at affald med animalsk indhold hygiejniseres (>70 C i 1 time) forud for anvendelse. Derfor har vi refokuseret vores indsats vedr. kompostering (WP2) for at kunne imødegå disse krav, og fået styrket indsatsen på området gennem en bevilling fra EU s LIFE instrument (se Annex 1). Dette skal muliggøre udvikling af en gårdkomposteringsteknologi (High temperature Low emission low cost) der kan sikre at det komposterede byaffald opnår en kvalitet der er i overensstemmelser med det fremtidige EU direktiv vedr. jordbrugsmæssig anvendelse af affald. Anbefaling forlængelse af projektperioden Da projektet skal etablere et langtidsforøg (WP1) og et biologisk jordkvalitets moniteringsprogram (WP5) ønsker vi at forlænge projektet frem til April 2006, i overensstemmelse med den oprindelige projektbeskrivelse, der tillod færdiggørelsen af 4 vækstsæsoner, samt påbegyndelsen af en 5 te. Den nuværende bevilling er tilstrækkelig til at sikre disse aktiviteter hvorfor vi anmoder om en no cost extension

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