Overview
This source page is a mechanical bulk-ingest record for a PDF in the research-pulls corpus. It preserves source-level identity, routeable product/analyte scope, and exact extracted numeric lines for later human or fresh-context audit. It does not derive HMTc thresholds, percentiles, or brand-by-brand comparisons.
Key numbers
The worker extracted the full PDF text with layout preservation twice and compared extraction hashes before commit. The following lines are copied from numeric/table-bearing regions of the PDF and retain the source units and wording where legible:
- feces contribute 70–80% of N and up to 60% of P in urban municipal wastewater (7, 8). In the
- fecal-oral pathway appears to be low (42, 43), there is a wide range of other pathogens
- as part of the large microbial content of feces: 25–54% of dry matter (DM) of feces consist
- pathogens are summarized in Table 1, and classified according to epidemiological risk:
- Table 1 Pathogens excreted with human feces and their epidemiological relevance according to the WHO (19)
- presented in Table 2. Of these, only Schistosoma haematobium poses a high epidemiological
- Table 2 Human urine-related pathogens and their epidemiological relevance (16, 19)
- Table 3 summarizes literature values for concentrations of heavy metals in human urine,
- leafy vegetables can absorb Cd from the soil during cultivation (74). In the case of tobacco in
- Table 3 Heavy metal content in human urine, feces, and other waste streams or recycling fertilizers. The values
- between 2002 and 2009 (82). This corresponds to an increase of ~30%, whereas the use of
- strated increases of several to 1,000% within 6 years (83). The pharmaceuticals also end up in
- Table 4 Ranges of concentrations of pharmaceutical residues in different substrates, where (n) depicts the number of data (11, 82, 99–104)
- stances. In summary, Table 4 shows that pharmaceutical loads in urine vary widely, which
- can shift the pharmaceutical contents towards the minimum values seen in Table 4 (ibid.).
- They found that RQ was far below 1 for trimethoprim and diclofenac, which means that the risk is
- Most relevant plant micro- and macronutrients can be found in urine and feces (Table 5).
- Humans excrete nutrients mostly via the urine: ~90% of N, 50 to 65% of P, and 50 to 80%
- Table 5 Nutrient contents in human urine, feces, and other waste streams or recycling fertilizers. The values
- Bio-waste compost (64, 66, 10.0±7.9 1.1±0.3 3.0±2.5 7.9±5.5 5.8±8.3 90 (n=1)
- trations (Table 5) (145). However, potential negative impacts on seed germination and
- proportion of N use efficiency compared to mineral NPK fertilizer, can reach 82% (152).
- (Table 6). Liquid materials can be pumped and can be spread using techniques that are already
- suitable (167). In general, following application, a superficial incorporation (e.g., with a
- Table 6 Proportion of DM in FM for human urine, feces, and other waste streams or recycling fertilizers. The
- Organic waste compost (64, 66, 127–129) 62.8±2.0 (n=5)
- Gardening waste compost (26, 66, 68, 70, 128–131) 53.3±11.7 (n=7)
- with a DM content of <2% of FM (176); (iv) low-emission application techniques such as drag
- important obstacle to direct application. It should be noted that NH3 loss as well as malodors
- Composting on a small scale (<5 m3 year−1) usually takes place in the mesophilic range
- paper were found in a range of 0.0018–0.180 μg g−1 and evaluated to be of minor importance
- horticultural suitability of operational additives. Table 7 summarizes the nutrient concentra-
- comparison to human feces and food waste, with about 35% and 45% of the DM, respectively
- Table 7 Nutrient contents in human urine and feces and in additives used for composting. The values are given
- materials and contributes to stable C build-up in the soil (237). This material can also improve
- (0–10 mm) and are largely free of extraneous materials should be used in vegetable
- Table 8 gives an overview of some environmentally relevant active substances in human
- Table 8 Active pharmaceutical substances from drugs for human use found in surface waters in Brandenburg
- Table 9 Pharmaceutical substances as indicator substances in sewage sludge analyses (109)
- manure from the UBA database (105) contained in Table 4:
- sewage treatment plants) and resulting database entries n=1 117
- & Solid manure (manure dung) was not shown in Table 4 for simplification, as it was largely
Methods (brief)
- source” is the use of dry toilets (DTs), in which human excreta are collected without or very
- properties of the contents collected in DTs and any processing-related additive, the focus of
- It should be noted that these classes of materials are not always collected separately, but
- content of pathogens, urine collected in urine-separating toilets can be more critical. Due to the
- feces, but also via vomit (19). However, the amounts of vomit collected in DTs is normally
- conditions, only small amounts of vomit are collected in DTs. The risk associated with fresh
- to injuries or with vomit make up a small amount of the total mass collected in the DT. It can
- feces collected in DTs will not only improve the quality of the derived fertilizers, but it will
- residues in human feces; data for separately collected urine (e.g., from separation toilets) were
- depends on whether the sample is from family homes, residential complexes, or public urinals.
- important obstacle to direct application. It should be noted that NH3 loss as well as malodors
- blood, or vomit. If toilet paper is not collected and disposed of separately, it becomes part of
- targeted elimination of pharmaceuticals from separately collected urine, e.g.,
- & Sample matrix (“matrix”):
- anaerobic digestion. Bioresour Technol 98. https://doi.org/10.1016/j.biortech.2006.02.039
- including anaerobic digestion of food waste and cultivation of vegetables on digestate in a bubble-insulated
- tion treatments: anaerobic and aerobic digestion, wastewater stabilization ponds and composting. Sci Total
- mass spectrometry. Anal Methods 9. https://doi.org/10.1039/c7ay01801k
Implications
This page makes the source discoverable for category-level evidence routing. Values remain source-native and should be used only with the stated matrix, species, basis, geography, and censoring context from the paper. The page does not convert total mercury to methylmercury or use total arsenic as inorganic arsenic.
Wiki pages this source may touch
- Fish — marine, non-predatory (sardines, anchovies, salmon, cod)
- Shellfish (shrimp, crab, lobster, clams, oysters, mussels)
- Root-Vegetable Purees
- Baby Wipes
- Cadmium
- Nickel
- Aluminum
- Chromium
Verification notes
- Identity check: DOI, raw handle, candidate cite-key, and SHA-256 were compared against existing
wiki/sources/pages before creation. - Full-PDF read:
pdftotext -layoutwas run on the full PDF twice; extracted text hashes matched before the page was written. - Numeric verification: numeric/table-bearing lines were selected mechanically from the verified extraction and preserved without unit conversion or rounding.
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Update history
The five most recent substantive edits to this page, classified major (evidence or structure moved), correction (a published value or statement was wrong and has been fixed), or minor (narrative rewritten without changing the underlying evidence). Each description is derived from what the edit did to this page; the linked commit is the authoritative record, routine regeneration passes are excluded, and the full version history lives in git. When DOI minting comes online (see schema docs), each entry below will also link to a version-pinned DataCite DOI.